CN104203835A - Functionalization of graphene holes for deionization - Google Patents
Functionalization of graphene holes for deionization Download PDFInfo
- Publication number
- CN104203835A CN104203835A CN201380014413.9A CN201380014413A CN104203835A CN 104203835 A CN104203835 A CN 104203835A CN 201380014413 A CN201380014413 A CN 201380014413A CN 104203835 A CN104203835 A CN 104203835A
- Authority
- CN
- China
- Prior art keywords
- ion
- solution
- functionalization
- hole
- graphene film
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B32/00—Carbon; Compounds thereof
- C01B32/15—Nano-sized carbon materials
- C01B32/182—Graphene
- C01B32/194—After-treatment
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D63/00—Apparatus in general for separation processes using semi-permeable membranes
- B01D63/10—Spiral-wound membrane modules
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D69/00—Semi-permeable membranes for separation processes or apparatus characterised by their form, structure or properties; Manufacturing processes specially adapted therefor
- B01D69/02—Semi-permeable membranes for separation processes or apparatus characterised by their form, structure or properties; Manufacturing processes specially adapted therefor characterised by their properties
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D69/00—Semi-permeable membranes for separation processes or apparatus characterised by their form, structure or properties; Manufacturing processes specially adapted therefor
- B01D69/10—Supported membranes; Membrane supports
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D71/00—Semi-permeable membranes for separation processes or apparatus characterised by the material; Manufacturing processes specially adapted therefor
- B01D71/02—Inorganic material
- B01D71/021—Carbon
- B01D71/0211—Graphene or derivates thereof
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B82—NANOTECHNOLOGY
- B82Y—SPECIFIC USES OR APPLICATIONS OF NANOSTRUCTURES; MEASUREMENT OR ANALYSIS OF NANOSTRUCTURES; MANUFACTURE OR TREATMENT OF NANOSTRUCTURES
- B82Y30/00—Nanotechnology for materials or surface science, e.g. nanocomposites
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B82—NANOTECHNOLOGY
- B82Y—SPECIFIC USES OR APPLICATIONS OF NANOSTRUCTURES; MEASUREMENT OR ANALYSIS OF NANOSTRUCTURES; MANUFACTURE OR TREATMENT OF NANOSTRUCTURES
- B82Y40/00—Manufacture or treatment of nanostructures
-
- C—CHEMISTRY; METALLURGY
- C01—INORGANIC CHEMISTRY
- C01B—NON-METALLIC ELEMENTS; COMPOUNDS THEREOF; METALLOIDS OR COMPOUNDS THEREOF NOT COVERED BY SUBCLASS C01C
- C01B32/00—Carbon; Compounds thereof
- C01B32/20—Graphite
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/469—Treatment of water, waste water, or sewage by electrochemical methods by electrochemical separation, e.g. by electro-osmosis, electrodialysis, electrophoresis
- C02F1/4691—Capacitive deionisation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2325/00—Details relating to properties of membranes
- B01D2325/14—Membrane materials having negatively charged functional groups
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2325/00—Details relating to properties of membranes
- B01D2325/16—Membrane materials having positively charged functional groups
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/08—Seawater, e.g. for desalination
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Nanotechnology (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Inorganic Chemistry (AREA)
- Materials Engineering (AREA)
- Physics & Mathematics (AREA)
- Condensed Matter Physics & Semiconductors (AREA)
- General Physics & Mathematics (AREA)
- Crystallography & Structural Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Hydrology & Water Resources (AREA)
- Composite Materials (AREA)
- Manufacturing & Machinery (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Geology (AREA)
- Health & Medical Sciences (AREA)
- Analytical Chemistry (AREA)
- Molecular Biology (AREA)
- Electrochemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Carbon And Carbon Compounds (AREA)
- Separation Using Semi-Permeable Membranes (AREA)
- Water Treatment By Electricity Or Magnetism (AREA)
Abstract
Description
发明领域field of invention
本发明涉及离子过滤,更具体地涉及利用石墨烯孔的功能化进行去离子化的方法和系统。The present invention relates to ion filtration, and more particularly to methods and systems for deionization utilizing the functionalization of graphene pores.
发明背景Background of the invention
随着淡水源日益变得缺乏,许多国家正在寻找可将盐水(最显著地是海水)转化成清洁的饮用水的方案。As fresh water sources become increasingly scarce, many countries are looking for solutions that can convert salt water, most notably sea water, into clean drinking water.
用于水脱盐的现有技术分成四大类,即,蒸馏、离子工艺、膜工艺以及结晶。这些技术中最有效且最常用的是多级闪急蒸馏(MSF)、多效蒸发(MEE)和逆渗透(RO)。成本是所有这些工艺的驱动因素,在这些工艺中能量和资金成本均是显著的。彻底开发了RO和MSF/MEE技术。当前,最佳的脱盐方案需要2至4倍的理论最小能量限度,所述理论最小能量限度通过水的简单蒸发而确立并且为3千焦/kg至7千焦/kg。蒸馏脱盐法包括多级闪蒸、多效蒸馏、蒸气压缩、太阳能增湿和地热脱盐。这些方法共享共同的途径,即改变水的状态以进行脱盐。这些途径使用热传递和/或真空压以蒸发盐水溶液。然后,将水蒸气冷凝并收集为淡水。Existing technologies for water desalination fall into four broad categories, namely, distillation, ionic processes, membrane processes, and crystallization. The most efficient and commonly used of these techniques are Multi-Stage Flash Distillation (MSF), Multiple Effect Evaporation (MEE) and Reverse Osmosis (RO). Cost is the driving factor for all of these processes, where both energy and capital costs are significant. Thoroughly developed RO and MSF/MEE technologies. Currently, optimal desalination schemes require 2 to 4 times the theoretical minimum energy limit established by simple evaporation of water and is 3 kJ/kg to 7 kJ/kg. Distillative desalination methods include multi-stage flash distillation, multiple-effect distillation, vapor compression, solar humidification and geothermal desalination. These approaches share a common pathway of changing the state of water for desalination. These approaches use heat transfer and/or vacuum pressure to evaporate the saline solution. Then, the water vapor is condensed and collected as fresh water.
离子工艺脱盐法集中于与溶液内离子的化学和电学相互作用。离子工艺脱盐法的实例包括离子交换、电渗析和电容去离子化。离子交换将固体聚合物离子交换剂或矿物质离子交换剂引入盐水溶液内。离子交换剂与溶液中期望的离子结合以使其可以易于滤出。电渗析是使用阳离子和阴离子选择性膜和电压电位以产生淡水和盐水溶液的交替通道的方法。电容去离子化使用电压电位以从溶液中带走带电荷的离子、捕获该离子并同时使水分子通过。Ionic process desalination methods focus on chemical and electrical interactions with ions in solution. Examples of ionic process desalination methods include ion exchange, electrodialysis, and capacitive deionization. Ion exchange introduces solid polymer ion exchangers or mineral ion exchangers into the brine solution. Ion exchangers bind desired ions in solution so that they can be easily filtered out. Electrodialysis is a process that uses cation- and anion-selective membranes and voltage potentials to create alternating passages of fresh water and saline solutions. Capacitive deionization uses a voltage potential to remove charged ions from solution, trap the ions and simultaneously pass water molecules.
膜脱盐工艺使用过滤和压力从溶液中除去离子。逆渗透(RO)是广泛使用的脱盐技术,其向盐水溶液施加压力以克服离子溶液的渗透压。压力推动水分子通过多孔膜进入淡水隔室,同时捕获离子,产生高浓度的盐水溶液。压力是这些方法的驱动成本因素,因为需要压力克服渗透压以捕获淡水。结晶脱盐是基于优先形成晶体而不包含离子的现象。通过以冰或甲醇(methyl hydrate)的形式产生结晶水,可以将纯净水与溶解的离子分离。在简单冷冻的情况下,使水冷却至其凝固点之下,由此产生冰。然后,将冰溶化以形成纯净水。甲醇结晶工艺使用甲烷气体滤过咸水溶液形成甲烷水合物,这发生在比水冷冻更低的温度。甲醇上升,促进分离,然后升温以分解成甲烷和脱盐的水。收集脱盐的水并重复利用甲烷。Membrane desalination processes use filtration and pressure to remove ions from solutions. Reverse osmosis (RO) is a widely used desalination technique that applies pressure to a brine solution to overcome the osmotic pressure of the ionic solution. The pressure pushes water molecules through the porous membrane into the freshwater compartment while trapping ions, creating a highly concentrated brine solution. Pressure is the driving cost factor for these methods because pressure is required to overcome osmotic pressure to capture fresh water. Crystallization desalination is based on the phenomenon of preferential formation of crystals that do not contain ions. Pure water can be separated from dissolved ions by generating water of crystallization in the form of ice or methyl hydrate. In the case of simple freezing, water is cooled below its freezing point, thereby producing ice. Then, the ice is melted to form pure water. The methanol crystallization process uses methane gas to filter a salty aqueous solution to form methane hydrate, which occurs at a lower temperature than water freezing. Methanol rises, facilitating the separation, and then heats up to break down into methane and desalinated water. The desalinated water is collected and methane is reused.
用于脱盐的蒸发和凝结通常被认为是节能的,但仍需要集中的热源。当进行大规模时,用于脱盐的蒸发和凝结通常与发电厂同地协作,并易受地理分布和尺寸的限制。Evaporation and condensation for desalination are generally considered energy efficient but still require a concentrated heat source. When done on a large scale, evaporation and condensation for desalination are often co-located with power plants and are subject to geographic distribution and size constraints.
电容去离子化不是广泛使用的,可能是因为电容电极趋于被除去的盐淤塞并需要频繁检修。所必需的电压易于依赖于板的间隔及流率,并且该电压可能成为危害物。Capacitive deionization is not widely used, probably because capacitive electrodes tend to become fouled with removed salts and require frequent maintenance. The necessary voltage tends to depend on the spacing of the plates and the flow rate, and this voltage can be a hazard.
逆渗透(RO)过滤器广泛用于水净化。RO过滤器使用多孔膜或半渗透膜,其通常由乙酸纤维素或聚酰亚胺薄膜复合物制成并通常具有1毫米(mm)的厚度。这些材料是亲水性的。膜通常被螺旋缠绕成管状形式以便于处理和膜支撑。膜呈现随机尺寸的孔径分布,其中最大尺寸的孔径足够小以允许水分子通过并且不允许或阻碍诸如溶解在水中的盐的离子通过。尽管典型的RO膜具有1毫米厚度,但RO膜的固有随机结构为流经该膜的水限定了长且迂回或曲折的路径,并且这些路径可以远大于1毫米长度。路径的长度和随机构造需要相当大的压力以将在表面处的水分子与离子剥离,然后使水分子逆着渗透压移动通过该膜。由此,RO过滤器趋于是能量低效的。Reverse osmosis (RO) filters are widely used for water purification. RO filters use porous or semi-permeable membranes, usually made of cellulose acetate or polyimide membrane composites and typically have a thickness of 1 millimeter (mm). These materials are hydrophilic. Membranes are usually helically wound into a tubular form for ease of handling and membrane support. The membrane exhibits a randomly sized pore size distribution, with the largest sized pores being small enough to allow water molecules to pass through and not to allow or block the passage of ions such as salts dissolved in water. Although a typical RO membrane has a thickness of 1 millimeter, the inherently random structure of RO membranes defines long and circuitous or tortuous paths for water flowing through the membrane, and these paths can be much greater than 1 millimeter in length. The length and random configuration of the pathways require considerable pressure to strip the water molecules from the ions at the surface and then move the water molecules through the membrane against osmotic pressure. As such, RO filters tend to be energy inefficient.
图1是RO膜10的横截面的抽象图示。在图1中,膜10限定了面向上游离子水溶液16的上游表面12以及下游表面14。将在上游侧上例示的离子选择为带+电荷的钠(Na)和带-电荷的氯(Cl)。钠被例示为与4个使离子变成溶剂化物的水分子(H2O)相缔合。每一水分子包括1个氧原子和2个氢(H)原子。在图1的RO膜10中水流动的路径20之一被例示为从上游表面12上的孔隙20u延伸至下游表面14上的孔隙20d。路径20例示为盘绕的,而不可能示出典型路径的真实的迂回曲折性质。此外,可以期望例示为20的路径与多个上游孔隙和多个下游孔隙相连。通过RO膜10的路径20可以不仅是盘绕的,而且其还可以随时间变化,因为一些孔隙被不可避免的碎片阻塞。FIG. 1 is an abstract illustration of a cross-section of an RO membrane 10 . In FIG. 1 , membrane 10 defines an upstream surface 12 facing an upstream aqueous ionic solution 16 and a downstream surface 14 . The ions exemplified on the upstream side are selected as +-charged sodium (Na) and --charged chlorine (Cl). Sodium is exemplified as being associated with 4 water molecules ( H2O ) that solvate the ion. Each water molecule includes 1 oxygen atom and 2 hydrogen (H) atoms. One of the paths 20 for water flow in the RO membrane 10 of FIG. 1 is illustrated as extending from pores 20u on the upstream surface 12 to pores 20d on the downstream surface 14 . Path 20 is illustrated as convoluted, and it is not possible to show the true tortuous nature of typical paths. Furthermore, it may be desirable for the path illustrated as 20 to connect with multiple upstream apertures and multiple downstream apertures. The path 20 through the RO membrane 10 may not only be coiled, but it may also vary over time as some pores become clogged with unavoidable debris.
期望可替代的水脱盐法和装置。Alternative water desalination methods and devices are desired.
发明概述Summary of the invention
公开了使溶液去离子化的方法,所述方法包括以下步骤:使石墨烯片的多个孔隙功能化以排斥所述溶液中的第一离子使其不运送通过所述经功能化的多个孔隙,未被传送的第一离子影响所述溶液中的第二离子使其不运送通过所述经功能化的多个孔隙;将所述石墨烯片置于溶液流动路径输入端和溶液流动路径输出端之间;以及使溶液进入所述溶液流动路径输入端并通过所述石墨烯片的经功能化的多个孔隙,由此产生在所述石墨烯片的溶液流动路径输出侧上的去离子化的溶液以及在所述石墨烯片的溶液流动路径输入侧上的包含第一离子和第二离子的第二溶液。A method of deionizing a solution is disclosed, the method comprising the step of functionalizing a plurality of pores of a graphene sheet to repel first ions in the solution from being transported through the functionalized plurality of pores. porosity, non-transported first ions affect second ions in the solution from being transported through the functionalized plurality of pores; placing the graphene sheet at the solution flow path input and solution flow path between the output ends; and allowing solution to enter the solution flow path input end and pass through the functionalized plurality of pores of the graphene sheet, thereby creating a depletion on the solution flow path output side of the graphene sheet The ionized solution and a second solution comprising first ions and second ions on the input side of the solution flow path of the graphene sheet.
在实施方案中,第一离子可以是带负电荷的离子,第二离子可以是带正电荷的离子,并且使多个孔隙功能化可以包括使所述多个孔隙的边缘(perimeter)功能化以具有负电荷,从而排斥所述溶液中带负电荷的离子。使多个孔隙的边缘功能化以具有负电荷可以包括使用氧、氮、磷、硫、氟、氯、溴或碘来使所述边缘功能化。或者,使多个孔隙的边缘功能化以具有负电荷可以包括使用具有整体负电荷的聚合物链或氨基酸链来使所述边缘功能化。在另一实施方案中,第一离子可以是带正电荷的离子,第二离子可以是带负电荷的离子,并且使多个孔隙功能化可以包括使所述多个孔隙的边缘功能化以具有正电荷,从而排斥所述溶液中带正电荷的离子。使多个孔隙的边缘功能化以具有正电荷可以包括使用硼、氢、锂、镁或铝来使所述边缘功能化。或者,使多个孔隙的边缘功能化以具有正电荷可以包括使用具有整体正电荷的聚合物链或氨基酸链来使所述边缘功能化。In embodiments, the first ion may be a negatively charged ion, the second ion may be a positively charged ion, and functionalizing the plurality of pores may include functionalizing the perimeters of the plurality of pores to has a negative charge, thereby repelling negatively charged ions in the solution. Functionalizing the edges of the plurality of pores to have a negative charge may include functionalizing the edges with oxygen, nitrogen, phosphorus, sulfur, fluorine, chlorine, bromine, or iodine. Alternatively, functionalizing the edges of the plurality of pores to have a negative charge may comprise functionalizing the edges with polymer chains or amino acid chains having an overall negative charge. In another embodiment, the first ions may be positively charged ions, the second ions may be negatively charged ions, and functionalizing the plurality of pores may include functionalizing the edges of the plurality of pores to have positively charged, thus repelling the positively charged ions in the solution. Functionalizing the edges of the plurality of pores to have a positive charge may include functionalizing the edges with boron, hydrogen, lithium, magnesium, or aluminum. Alternatively, functionalizing the edges of the plurality of pores to have a positive charge may comprise functionalizing the edges with polymer chains or amino acid chains having an overall positive charge.
用于去离子化的方法可以还包括限定所述石墨烯片的多个孔隙的尺寸以抵制所述第一离子的运送。所述方法可以还包括向石墨烯片施加电荷,其中所述电荷排斥第一离子。The method for deionization may further include sizing the plurality of pores of the graphene sheet to resist transport of the first ions. The method may further include applying a charge to the graphene sheet, wherein the charge repels the first ion.
公开了使溶液去离子化的方法,所述方法包括以下步骤:使第一石墨烯片的第一多个孔隙功能化以排斥所述溶液中的第一离子使其不运送通过所述经功能化的第一多个孔隙,未被运送的第一离子还影响所述溶液中的第二离子使其不运送通过所述经功能化的第一多个孔隙;使第二石墨烯片的第二多个孔隙功能化以排斥所述溶液中的第二离子使其不运送通过所述经功能化的第二多个孔隙,未被运送的第二离子还影响所述溶液中的第一离子使其不运送通过所述经功能化的第二多个孔隙;将所述第一石墨烯片置于溶液流动路径输入端的下游并且将所述第二石墨烯片置于所述第一石墨烯片和溶液流动路径输出端之间;以及使溶液进入所述溶液流动路径输入端,通过所述第一石墨烯片,然后通过所述第二石墨烯片,由此在所述溶液流动路径输出端处产生去离子化的溶液。A method of deionizing a solution is disclosed, the method comprising the step of: functionalizing a first plurality of pores of a first graphene sheet to repel first ions in the solution from being transported through the functionalized The non-transported first ions also affect the second ions in the solution from being transported through the functionalized first plurality of pores; making the second graphene sheet the first plurality of pores Two plurality of pores functionalized to repel second ions in the solution from transport through the functionalized second plurality of pores, the non-transported second ions also affecting the first ions in the solution not transporting through the functionalized second plurality of pores; placing the first graphene sheet downstream of the solution flow path input and placing the second graphene sheet at the first graphene between the sheet and the solution flow path output; and allowing solution to enter the solution flow path input, pass through the first graphene sheet, and then pass through the second graphene sheet, thereby at the solution flow path output A deionized solution is produced at the end.
在实施方案中,第一离子是带负电荷的离子,第二离子是带正电荷的离子,使第一多个孔隙功能化包括使所述第一多个孔隙的第一边缘功能化以具有负电荷从而排斥溶液中的带负电荷的离子,并且使第二多个孔隙功能化包括使所述第二多个孔隙的第二边缘功能化以具有正电荷从而排斥所述溶液中的带正电荷的离子。使第一多个孔隙的第一边缘功能化以具有负电荷可以包括使用氧、氮、磷、硫、氟、氯、溴或碘来使所述第一多个孔隙的第一边缘功能化。或者,使第一多个孔隙的第一边缘功能化以具有负电荷可以包括使用具有整体负电荷的聚合物链或氨基酸链来使所述第一边缘功能化。使第二多个孔隙的第二边缘功能化以具有正电荷可以包括使用硼、氢、锂、镁或铝来使所述第二边缘功能化。或者,使第二多个孔隙的第二边缘功能化以具有正电荷可以包括使用具有整体正电荷的聚合物链或氨基酸链来使所述第二边缘功能化。In embodiments, the first ions are negatively charged ions and the second ions are positively charged ions, and functionalizing the first plurality of pores includes functionalizing the first edges of the first plurality of pores to have Negatively charged to repel negatively charged ions in the solution, and functionalizing the second plurality of pores includes functionalizing a second edge of the second plurality of pores to have a positive charge to repel positively charged ions in the solution. charged ions. Functionalizing the first edges of the first plurality of pores to have a negative charge may include functionalizing the first edges of the first plurality of pores with oxygen, nitrogen, phosphorus, sulfur, fluorine, chlorine, bromine, or iodine. Alternatively, functionalizing the first edge of the first plurality of pores to have a negative charge may comprise functionalizing the first edge with polymer chains or amino acid chains having an overall negative charge. Functionalizing the second edges of the second plurality of pores to have a positive charge may include functionalizing the second edges with boron, hydrogen, lithium, magnesium, or aluminum. Alternatively, functionalizing the second edges of the second plurality of pores to have a positive charge may comprise functionalizing the second edges with polymer chains or amino acid chains having an overall positive charge.
在另一实施方案中,第一离子是带正电荷的离子,第二离子是带负电荷的离子,使第一多个孔隙功能化包括使所述第一多个孔隙的第一边缘功能化以具有正电荷从而排斥溶液中的带正电荷的离子,并且使第二孔隙功能化包括使第二多个孔隙的第二边缘功能化以具有负电荷从而排斥所述溶液中的带负电荷的离子。使第二多个孔隙的第二边缘功能化以具有负电荷可以包括使用氧、氮、磷、硫、氟、氯、溴或碘来使所述第二边缘功能化。或者,使第二多个孔隙的第二边缘功能化以具有负电荷可以包括使用具有整体负电荷的聚合物链或氨基酸链来使所述第二边缘功能化。使第一多个孔隙的第一边缘功能化以具有正电荷可以包括使用硼、氢、锂、镁或铝来使所述第一边缘功能化。或者,使第一多个孔隙的第一边缘功能化以具有正电荷包括使用具有整体正电荷的聚合物链或氨基酸链来使所述第一边缘功能化。In another embodiment, the first ions are positively charged ions and the second ions are negatively charged ions, and functionalizing the first plurality of pores includes functionalizing a first edge of the first plurality of pores to have a positive charge to repel positively charged ions in the solution, and functionalizing the second pores includes functionalizing a second edge of the second plurality of pores to have a negative charge to repel negatively charged ions in the solution. ion. Functionalizing the second edges of the second plurality of pores to have a negative charge may include functionalizing the second edges with oxygen, nitrogen, phosphorus, sulfur, fluorine, chlorine, bromine, or iodine. Alternatively, functionalizing the second edges of the second plurality of pores to have a negative charge may comprise functionalizing the second edges with polymer chains or amino acid chains having an overall negative charge. Functionalizing the first edges of the first plurality of pores to have a positive charge may include functionalizing the first edges with boron, hydrogen, lithium, magnesium, or aluminum. Alternatively, functionalizing the first edge of the first plurality of pores to have a positive charge comprises functionalizing the first edge with polymer chains or amino acid chains having an overall positive charge.
所述方法可以还包括限定第一石墨烯片的第一多个孔隙的尺寸以抵制第一离子的运送,并且限定所述第二石墨烯片的第二多个孔隙的尺寸以抵制第二离子的运送。所述方法还可以包括向第一石墨烯片施加第一电荷以及向第二石墨烯片施加第二电荷,其中所述第一电荷排斥第一离子以及所述第二电荷排斥第二离子。The method may further include sizing a first plurality of pores of the first graphene sheet to repel transport of a first ion, and sizing a second plurality of pores of the second graphene sheet to repel second ions delivery. The method may also include applying a first charge to the first graphene sheet and applying a second charge to the second graphene sheet, wherein the first charge repels the first ion and the second charge repels the second ion.
公开了去离子器,其包括:具有多个孔隙的石墨烯片,所述多个孔隙经功能化以排斥溶液中第一离子使其不运送通过所述多个孔隙,未被运送的第一离子影响所述溶液中的第二离子使其不运送通过经功能化的多个孔隙;具有输入端和输出端的溶液流动路径,其中所述石墨烯片被放置在所述溶液流动路径输入端和所述溶液流动路径输出端之间;以及负载有离子的溶液的源。将负载有离子的溶液引入溶液流动路径输入端,经过所述石墨烯片,由此产生在所述石墨烯片的溶液流动路径输入侧上的包含第一离子和第二离子的第一离子溶液以及在所述石墨烯片的溶液流动路径输出侧上的去离子化的溶液。A deionizer is disclosed comprising: a graphene sheet having a plurality of pores functionalized to repel first ions in solution from being transported through the plurality of pores, the first ions not being transported ions affecting a second ion in the solution from transport through the functionalized plurality of pores; a solution flow path having an input and an output, wherein the graphene sheet is placed between the solution flow path input and between the solution flow path outputs; and a source of ion-laden solution. introducing a solution laden with ions into a solution flow path input end, past the graphene sheet, thereby producing a first ionic solution comprising first ions and second ions on the solution flow path input side of the graphene sheet and deionized solution on the output side of the solution flow path of the graphene sheet.
在实施方案中,第一离子是带负电荷的离子,第二离子是带正电荷的离子,并且经功能化的多个孔隙包括具有带负电荷的边缘的多个孔隙以排斥溶液中的带负电荷的离子。在另一实施方案中,第一离子是带正电荷的离子,第二离子是带负电荷的离子,并且经功能化的多个孔隙包括具有带正电荷的边缘的多个孔隙以排斥溶液中的带正电荷的离子。In an embodiment, the first ion is a negatively charged ion, the second ion is a positively charged ion, and the plurality of pores functionalized includes a plurality of pores with negatively charged edges to repel charged ions in solution. negatively charged ions. In another embodiment, the first ion is a positively charged ion, the second ion is a negatively charged ion, and the plurality of pores functionalized includes a plurality of pores with positively charged edges to repel positively charged ions.
去离子器可以还包括经限定尺寸以抵制第一离子的运送的石墨烯片的多个孔隙。去离子器可以还包括使石墨烯片带有电荷,所述电荷排斥第一离子。The deionizer may further include a plurality of pores of the graphene sheet sized to resist transport of the first ions. The deionizer may further include charging the graphene sheet with a charge that repels the first ions.
公开了溶液去离子器,其包括:具有第一多个孔隙的第一石墨烯片,所述第一多个孔隙经功能化以排斥第一离子使其不运送通过所述经功能化的第一多个孔隙,未被运送的第一离子影响所述溶液中的第二离子使其不运送通过所述经功能化的第一多个孔隙;具有第二多个孔隙的第二石墨烯片,所述第二多个孔隙经功能化以排斥所述溶液中的所述第二离子使其不运送通过所述经功能化的第二多个孔隙,未被运送的第二离子影响所述溶液中的第一离子使其不运送通过所述经功能化的第二多个孔隙;具有输入端和输出端的溶液流动路径,其中所述第一石墨烯片处于所述溶液流动路径输入端的下游,并且所述第二石墨烯片处于所述第一石墨烯片和所述溶液流动路径输出端之间;以及负载有离子的溶液的源。将负载有离子的溶液引入溶液流动路径输入端,经过第一石墨烯片,然后经过第二石墨烯片,由此在溶液流动路径输出端产生去离子化的溶液。A solution deionizer is disclosed comprising: a first graphene sheet having a first plurality of pores functionalized to repel first ions from transport through the functionalized first a plurality of pores through which non-transported first ions affect second ions in the solution from being transported through the functionalized first plurality of pores; a second graphene sheet having a second plurality of pores , the second plurality of pores are functionalized to repel the second ions in the solution from being transported through the functionalized second plurality of pores, the non-transported second ions affecting the first ions in solution prevent transport through said functionalized second plurality of pores; a solution flow path having an input and an output, wherein said first graphene sheet is downstream of said solution flow path input , and the second graphene sheet is between the first graphene sheet and the solution flow path output; and a source of ion-laden solution. A solution laden with ions is introduced at the input of the solution flow path, through the first graphene sheet, and then through the second graphene sheet, thereby producing a deionized solution at the output of the solution flow path.
在实施方案中,第一离子是带负电荷的离子,第二离子是带正电荷的离子,经功能化的第一多个孔隙包括具有排斥溶液中带负电荷的离子的带负电荷的边缘的第一多个孔隙,并且经功能化的第二多个孔隙包括具有排斥溶液中带正电荷的离子的带正电荷的边缘的第二多个孔隙。在另一实施方案中,第一离子是带正电荷的离子,第二离子是带负电荷的离子,经功能化的第一多个孔隙包括具有排斥溶液中带正电荷的离子的带正电荷的边缘的第一多个孔隙,并且经功能化的第二多个孔隙包括具有排斥溶液中带负电荷的离子的带负电荷的边缘的第二多个孔隙。In embodiments, the first ions are negatively charged ions, the second ions are positively charged ions, and the functionalized first plurality of pores includes negatively charged edges that repel negatively charged ions in solution The first plurality of pores, and the functionalized second plurality of pores includes a second plurality of pores having positively charged edges that repel positively charged ions in solution. In another embodiment, the first ions are positively charged ions, the second ions are negatively charged ions, and the functionalized first plurality of pores includes positively charged ions that repel positively charged ions in solution. and the functionalized second plurality of pores includes a second plurality of pores having negatively charged edges that repel negatively charged ions in solution.
所述溶液去离子器可以还包括经限定尺寸以抵制第一离子运送的第一石墨烯片的第一多个孔隙以及经限定尺寸以抵制第二离子运送的第二石墨烯片的第二多个孔隙。所述溶液去离子器可以还包括带有第一电荷的第一石墨烯片和带有第二电荷的第二石墨烯片,其中所述第一电荷排斥第一离子且所述第二电荷排斥第二离子。The solution deionizer may further include a first plurality of pores of the first graphene sheet sized to resist transport of the first ion and a second plurality of pores of the second graphene sheet sized to resist transport of the second ion. pores. The solution deionizer may further include a first graphene sheet with a first charge and a second graphene sheet with a second charge, wherein the first charge repels the first ions and the second charge repels second ion.
附图简述Brief description of the drawings
图1是现有技术的逆渗透(RO)过滤膜的抽象横截面图示;Figure 1 is an abstract cross-sectional illustration of a prior art reverse osmosis (RO) filtration membrane;
图2是本公开一方面的使用穿孔的石墨烯片的水过滤器的抽象图示;2 is an abstract illustration of a water filter using perforated graphene sheets in accordance with an aspect of the present disclosure;
图3是可用于图2的布置方案中的穿孔的石墨烯片的平面图示,示出多个孔隙之一的形状;Figure 3 is a plan view of a perforated graphene sheet useful in the arrangement of Figure 2, showing the shape of one of the plurality of pores;
图4是穿孔的石墨烯片的平面图,示出经功能化的穿孔或孔隙及尺寸;Figure 4 is a plan view of a perforated graphene sheet showing functionalized perforations or pores and their dimensions;
图5是可与图2的穿孔的石墨烯片联合使用的背衬片的平面图示;Figure 5 is a plan view of a backing sheet that may be used in conjunction with the perforated graphene sheet of Figure 2;
图6是本公开一方面的水去离子过滤器的抽象图示,其使用多个穿孔的石墨烯片;以及6 is an abstract illustration of a water deionization filter using a plurality of perforated graphene sheets in accordance with an aspect of the present disclosure; and
图7是示出通常对应于图6的布置方案的管道布置方案的简化图,其中穿孔的石墨烯片被螺旋缠绕并封装在圆筒中。Fig. 7 is a simplified diagram showing a piping arrangement generally corresponding to that of Fig. 6, in which perforated graphene sheets are helically wound and packaged in a cylinder.
详细描述A detailed description
图2是根据示例性实施方案或本公开一方面的基础去离子化装置200的抽象图示。在图2中,通道210将负载有离子的水输送至安置在支撑室214中的过滤膜212。负载有离子的水可以例如为海水或咸水。在一示例性实施方案中,可以以已知方式将过滤膜212缠绕成螺旋形。可以由罐216通过重力或由泵218提供流经图2的通道210的负载有离子的水的流动动力或压力。阀236和238允许选择负载有离子的水的源。在装置或布置方案200中,过滤膜212是具有穿孔(还称为孔隙)的穿孔的石墨烯片。石墨烯是单原子层厚的碳原子层,其结合在一起以限定片310,如图3所示。单石墨烯片的厚度为约0.2纳米(nm)。实际上,认为单石墨烯片的厚度为约0.2纳米至0.3纳米,并且具体为约0.23纳米。可以形成具有更大厚度的多个石墨烯片。图3的石墨烯片310的碳原子限定了由6个碳原子构成的六方环结构(苯环)的重复图案,所述结构形成碳原子的蜂巢晶格。由该片中的各个6-碳原子环结构形成间隙孔隙308(interstitial aperture),并且该间隙孔隙跨度(across)小于1纳米。实际上,技术人员会认识到间隙孔隙被认为在其最长尺寸上跨度约0.23纳米。该尺寸过小而不能使水或离子通过。FIG. 2 is an abstract illustration of a basic deionization apparatus 200 according to an exemplary embodiment or aspect of the disclosure. In FIG. 2 , channels 210 deliver ion-laden water to a filter membrane 212 disposed in a support chamber 214 . The ion-loaded water may be, for example, seawater or brackish water. In an exemplary embodiment, filter membrane 212 may be wound in a helical shape in known manner. Flow momentum or pressure for the ion-laden water flowing through channel 210 of FIG. 2 may be provided by tank 216 by gravity or by pump 218 . Valves 236 and 238 allow selection of a source of ion-laden water. In the device or arrangement 200, the filter membrane 212 is a perforated graphene sheet having perforations (also referred to as pores). Graphene is a monoatomic layer thick layer of carbon atoms bonded together to define a sheet 310 as shown in FIG. 3 . The thickness of a single graphene sheet is about 0.2 nanometers (nm). In practice, the thickness of a single graphene sheet is believed to be about 0.2 nm to 0.3 nm, and specifically about 0.23 nm. Multiple graphene sheets with greater thickness can be formed. The carbon atoms of the graphene sheet 310 of FIG. 3 define a repeating pattern of hexagonal ring structures (benzene rings) composed of 6 carbon atoms that form a honeycomb lattice of carbon atoms. Interstitial apertures 308 are formed by each 6-carbon atom ring structure in the sheet, and the interstitial apertures are less than 1 nanometer across. In practice, the skilled artisan will recognize that interstitial pores are believed to span about 0.23 nanometers in their longest dimension. The size is too small to pass water or ions.
图2的去离子化装置具有从水源201或216至通道210的溶液流动路径,所述通道210可以被认为是溶液流动路径的输入端。从通道210起,溶液流动路径延伸至室214的溶液流动路径输入侧,然后通过石墨片212,然后达到室214的溶液流动路径输出侧,并最终达到通道222,所述通道222被认为是溶液流动路径的输出端。可以通过泵218或由罐216通过重力供给来加压携带了不期望的离子的水201,由此产生加压的水。将所述加压的水施用于穿孔的石墨烯212的第一侧212u,以使水分子流至穿孔的石墨烯片的第二侧212I。The deionization device of Figure 2 has a solution flow path from a water source 201 or 216 to a channel 210, which can be considered as the input of the solution flow path. From channel 210, the solution flow path extends to the solution flow path input side of chamber 214, then through graphite sheet 212, then to the solution flow path output side of chamber 214, and finally to channel 222, which is considered the solution flow path output of the flow path. Water 201 laden with undesired ions may be pressurized by pump 218 or by gravity feed from tank 216, thereby producing pressurized water. The pressurized water is applied to the first side 212u of the perforated graphene 212 to cause water molecules to flow to the second side 2121 of the perforated graphene sheet.
为了形成图2的穿孔的石墨烯片212,制成一个或多个穿孔,如图3所示。通过石墨烯片310限定了典型的大致圆形或标称圆形的孔隙312。在实施方案中,孔隙312具有约2纳米的标称直径。选择2-纳米尺寸以允许通常被预期存在于盐水或咸水中的最大离子运送通过孔隙,所述最大离子为氯离子。在一些实施方案中,孔隙312的标称直径可以为0.8nm至1.2nm。然而,本文详述的孔隙的边缘的功能化取决于排斥离子以使其不运送通过孔隙,即使该孔隙以其它方式被改变尺寸以允许离子的运送。以下事实影响孔隙312的大致圆形的形状,即,石墨烯片310的六方碳环结构部分地限定了孔隙的边界。To form the perforated graphene sheet 212 of FIG. 2 , one or more perforations are made, as shown in FIG. 3 . A typically substantially circular or nominally circular aperture 312 is defined by the graphene sheet 310 . In an embodiment, pores 312 have a nominal diameter of about 2 nanometers. The 2-nanometer size is chosen to allow transport through the pores of the largest ion typically expected to be present in brine or brackish water, which is chloride. In some embodiments, pores 312 may have a nominal diameter of 0.8 nm to 1.2 nm. However, the functionalization of the edges of the pores as detailed herein depends on repelling ions from being transported through the pore, even if the pore is otherwise resized to allow transport of ions. The generally circular shape of the pores 312 is influenced by the fact that the hexagonal carbon ring structure of the graphene sheet 310 partially defines the boundaries of the pores.
可以通过选择性氧化来制成孔隙312,所述选择性氧化意指暴露于氧化剂一段所选的时段。认为孔隙312还可以是激光钻孔的。如出版物Nano Lett.2008,Vol.8,no.7,pg 1965-1970所述,最直接的穿孔策略是在高温下用在氩气中稀释的氧处理石墨烯膜。如其中所述,在500℃下使用在1个大气(atm)的氩气中350mTorr的氧在石墨烯中蚀刻20nm至180nm范围的穿过的孔隙或孔,持续2小时。该论文合理地建议了孔的数量与石墨烯片的缺陷有关,并且孔的尺寸与停留时间有关。其被认为是在石墨烯结构中制造所期望的穿孔的优选方法。该结构可以是石墨烯纳米板和石墨烯纳米带。因此,可以通过更短的氧化时间来形成在期望范围内的孔隙。另一更相关的方法利用自组装的聚合物,该聚合物产生适于使用反应性离子蚀刻进行图案化的掩模。P(S-嵌段MMA)嵌段共聚物形成一列PMMA柱,其经重建形成RIE的过孔(vias)。孔的图案是非常密集的。由PMMA嵌段(PMMA block)的分子量和P(S-MMA)中PMMA的重量分数来控制孔的数量和尺寸。任一方法具有产生穿孔的石墨烯片的可能性。Pores 312 may be made by selective oxidation, which means exposure to an oxidizing agent for a selected period of time. It is contemplated that the apertures 312 may also be laser drilled. As described in the publication Nano Lett. 2008, Vol. 8, no. 7, pg 1965-1970, the most straightforward perforation strategy is to treat graphene membranes with oxygen diluted in argon at high temperature. As described therein, through pores or pores ranging from 20 nm to 180 nm were etched in graphene using 350 mTorr of oxygen in 1 atmosphere (atm) of argon at 500° C. for 2 hours. The paper reasonably suggests that the number of pores is related to the defects of the graphene sheet, and that the size of the pores is related to the residence time. It is considered to be the preferred method to create the desired perforations in the graphene structure. The structures can be graphene nanoplates and graphene nanoribbons. Therefore, pores within a desired range can be formed by a shorter oxidation time. Another, more related approach utilizes self-assembled polymers that produce masks suitable for patterning using reactive ion etching. The P(S-block MMA) block copolymer forms an array of PMMA pillars that are reconstructed to form the vias of the RIE. The hole pattern is very dense. The number and size of pores are controlled by the molecular weight of PMMA block (PMMA block) and the weight fraction of PMMA in P (S-MMA). Either method has the potential to produce perforated graphene sheets.
可以用带特定电荷的官能团使孔隙的边缘功能化。边缘周围的带电荷的基团会排斥相似电荷的离子,增加带相似电荷的离子运送通过孔隙的活化能垒。此外,相反电荷的离子会受影响而与未被运送的离子一起滞留。正离子和负离子的分离会需要大量的输入系统的能量,这不是本发明的特征。因此,通过排斥相似电荷的离子以使其不运送通过经功能化的孔隙,也有效地排斥了相反电荷的离子使其不运送通过经功能化的孔隙。在实施方案中,可以用氧来使孔隙的边缘功能化,所述氧为带负电荷的离子。具有被氧功能化的孔隙的片会排斥带负电荷的氯离子,这会使氯离子以非常低的速率运送通过该孔隙或根本不通过该孔隙。带正电荷的钠离子会受影响以与被排斥的氯离子一起滞留在室226内。在其他实施方案中,可以使用除氧之外的其它元素,通过负电荷来功能化孔隙的边缘。例如,在实施方案中,可以使用氮、磷、硫、氟、氯、溴和碘中的至少一种来与负电荷一起用于使边缘功能化。The edges of the pores can be functionalized with specifically charged functional groups. Charged groups around the edges repel similarly charged ions, increasing the activation barrier for similarly charged ions to transport through the pore. In addition, ions of opposite charge can be affected to remain with ions that were not transported. Separation of positive and negative ions would require a large amount of energy input into the system, which is not a feature of the present invention. Thus, by repelling similarly charged ions from transport through the functionalized pores, oppositely charged ions are effectively also repelled from transport through the functionalized pores. In embodiments, the edges of the pores may be functionalized with oxygen, which is a negatively charged ion. Sheets with pores functionalized with oxygen will repel the negatively charged chloride ions, which will cause the chloride ions to be transported through the pores at a very low rate or not at all. Positively charged sodium ions are influenced to remain within chamber 226 along with the repelled chloride ions. In other embodiments, elements other than oxygen can be used to functionalize the edges of the pores with a negative charge. For example, in embodiments, at least one of nitrogen, phosphorous, sulfur, fluorine, chlorine, bromine, and iodine may be used to functionalize the edges along with negative charges.
因此,如果片212的孔隙的边缘带电荷以排斥一种电荷的离子,则相反电荷的离子也可能受影响而不通过该片。尽管可以通过向系统内输入大量的能量来使相反电荷的离子通过片的孔隙,但预期的是,向系统添加此量的能量会产生在去离子化的情形中不期望的反应(例如产生氯气或氢气)。Thus, if the edges of the pores of sheet 212 are charged to repel ions of one charge, ions of the opposite charge may also be affected and not pass through the sheet. Although it is possible to pass oppositely charged ions through the pores of the sheet by inputting large amounts of energy into the system, it is expected that adding this amount of energy to the system would produce reactions that are undesirable in the case of deionization (e.g., generation of chlorine gas). or hydrogen).
如所理解的,在另一实施方案中,边缘可以带有带正电荷的离子,例如硼。具有被硼功能化的孔隙的片会使带正电荷的钠离子以非常低的速率通过该孔隙或根本不通过该孔隙。带负电荷的氯离子会趋于与钠离子一起滞留并还会以非常低的速率通过孔隙或根本不通过该孔隙。在其他实施方案中,可以使用除硼之外的其它元素,用正电荷来功能化孔隙的边缘。例如,在实施方案中,可以使用氢、锂、镁和铝中的至少一种来与正电荷一起用于使边缘功能化。As will be appreciated, in another embodiment the edges may carry positively charged ions such as boron. Sheets with pores functionalized with boron will allow positively charged sodium ions to pass through the pores at a very low rate or not at all. The negatively charged chloride ions will tend to stay with the sodium ions and also pass through the pores at a very low rate or not at all. In other embodiments, elements other than boron can be used to functionalize the edges of the pores with a positive charge. For example, in embodiments, at least one of hydrogen, lithium, magnesium, and aluminum may be used to functionalize the edges along with a positive charge.
在另一实施方案中,可以使用具有整体正电荷或整体负电荷的聚合物链或氨基酸链来功能化孔隙的边缘。一些候选的聚合物包括聚氧化乙烯、聚磺酰亚胺类聚合物、金-硫醇嵌体、基于钌的有机金属化合物以及电解聚合物。聚合物链或氨基酸链的使用可以允许更能控制孔隙边缘上的电荷强度,由此允许一定程度控制经功能化的孔隙的排斥和/或吸引作用。电荷强度可以是重要的,其取决于需要被石墨烯片过滤的离子的类型。In another embodiment, the edges of the pores can be functionalized with polymer chains or amino acid chains having an overall positive charge or an overall negative charge. Some candidate polymers include polyethylene oxide, polysulfonimide-based polymers, gold-thiol interlayers, ruthenium-based organometallic compounds, and electrolytic polymers. The use of polymer chains or amino acid chains may allow greater control of the charge strength on the pore edges, thereby allowing some control over the repulsion and/or attraction of the functionalized pores. The charge strength can be important depending on the type of ions that need to be filtered by the graphene sheet.
可以通过多种通常已知的方法来实现孔隙的功能化。在实施方案中,可以通过使用对氧具有反应性的化学制品或基团对石墨烯片进行引晶,然后将该片暴露于氧等离子体,由此使该化学制品或基团反应并在石墨烯片中产生经功能化的孔,从而产生在石墨烯片上的经功能化的孔隙。在另一实施方案中,可以通过向现有孔隙的边缘应用对诸如电荷或光脉冲等外部刺激有反应性的化学官能团,然后将该片暴露于电荷或光脉冲,由此使该化学基团连接至该边缘,从而形成经功能化的孔隙。酸处理、反应性离子蚀刻或标准有机化学技术也可以用于使孔隙的边缘功能化。功能化的方法包括但不限于:反应性离子和分子物质,例如四氟化碳等离子体、氧等离子体、原子氧、氮等离子体和原子氮。在结构中最初产生缺陷之后的材料的功能化取决于在该材料上剩余的化学成分:例如,如果将氮或氧反应性基团连接至该材料,则该材料可以与有机酰基氯反应以在材料和官能团之间产生酯连接或酰胺连接。与材料连接的官能团可以是会支持连接物官能度的任何物质。Functionalization of the pores can be achieved by a variety of generally known methods. In an embodiment, the graphene sheet can be seeded with a chemical or group that is reactive with oxygen and then exposed to an oxygen plasma, whereby the chemical or group reacts and forms a Functionalized pores are created in the ene sheet, resulting in functionalized pores on the graphene sheet. In another embodiment, chemical functional groups that are responsive to external stimuli, such as electric charge or light pulses, can be rendered functional by applying them to the edges of existing pores and then exposing the sheet to charge or light pulses. connected to this edge, forming a functionalized pore. Acid treatment, reactive ion etching, or standard organic chemistry techniques can also be used to functionalize the edges of the pores. Methods of functionalization include, but are not limited to: reactive ions and molecular species such as carbon tetrafluoride plasma, oxygen plasma, atomic oxygen, nitrogen plasma, and atomic nitrogen. The functionalization of the material after the initial defect in the structure is dependent on the chemical composition remaining on the material: for example, if a nitrogen or oxygen reactive group is attached to the material, the material can react with an organic acid chloride to An ester linkage or an amide linkage occurs between the material and the functional group. The functional group attached to the material can be anything that would support the functionality of the linker.
如所述的那样,图3的石墨烯片310具有仅为单原子的厚度。因此,该片趋于是挠性的。可以通过向片212施用背衬结构来改善石墨烯片的弯曲。在图2中,穿孔的石墨烯片212的背衬结构例示为220。在此实施方案中,背衬结构220是穿孔的聚四氟乙烯(有时称为聚四氟乙烷)的片。背衬片的厚度可以例如为1毫米(mm)。As stated, the graphene sheet 310 of FIG. 3 has a thickness of only one atom. Therefore, the sheet tends to be flexible. The bending of the graphene sheet can be improved by applying a backing structure to the sheet 212 . The backing structure of the perforated graphene sheet 212 is illustrated as 220 in FIG. 2 . In this embodiment, the backing structure 220 is a sheet of perforated polytetrafluoroethylene (sometimes referred to as polytetrafluoroethylene). The thickness of the backing sheet may be, for example, 1 millimeter (mm).
应注意,在图2的装置或布置方案中,可以由罐216通过重力提供通过路径210向穿孔的膜212施加的负载有离子的水的压力,由此强调装置200的方面之一。即,与RO膜不同,形成穿孔的膜的穿孔的石墨烯片310(图3)是疏水性的,并且经过穿通的孔隙(图2和3的312)的水不受吸引力(归因于湿润)的阻碍。此外,如所述的那样,在石墨烯片310中通过孔隙312的流动路径的长度等于片的厚度,所述厚度为约0.2nm。该长度远小于延伸通过RO膜的随机路径的长度。因此,需要非常小的压力来提供流体流动,或相反地,在穿孔的石墨烯片310中,在给定压力下的流动远远大得多。这进而转化成离子分离的低能量需求。认为RO膜中使水逆着渗透压而通过该膜所需要的压力包括摩擦组分,其导致膜变热。因此,必须向RO膜施加的压力中有一些压力未用于克服渗透压,反而变成热量。模拟的结果表明穿孔的石墨烯片使所需的压力降低了至少5倍。因此,在RO膜可能在上游侧需要40磅/平方英尺(PSI)的压强以实现具有特定离子浓度的去离子水的特定流动的情况下,穿孔的石墨烯片对于相同的流率可需要8PSI以下。It should be noted that in the device or arrangement of FIG. 2 , the pressure of the ion-laden water applied through path 210 to perforated membrane 212 may be provided by gravity from tank 216 , thereby emphasizing one of the aspects of device 200 . That is, unlike RO membranes, the perforated graphene sheets 310 ( FIG. 3 ) forming the perforated membranes are hydrophobic, and water passing through the perforated pores ( 312 of FIGS. 2 and 3 ) is not attractive (due to Humidity) hindrance. Furthermore, as noted, the length of the flow path through the pores 312 in the graphene sheet 310 is equal to the thickness of the sheet, which is about 0.2 nm. This length is much smaller than the length of a random path extending through the RO membrane. Therefore, very little pressure is required to provide fluid flow, or conversely, in the perforated graphene sheet 310, the flow at a given pressure is much greater. This in turn translates into low energy requirements for ion separation. It is believed that the pressure required in an RO membrane to move water through the membrane against the osmotic pressure includes a frictional component which causes the membrane to heat up. Therefore, some of the pressure that must be applied to the RO membrane is not used to overcome the osmotic pressure, but instead becomes heat. Simulations showed that the perforated graphene sheets reduced the required pressure by at least a factor of five. Thus, where a RO membrane may require 40 pounds per square foot (PSI) of pressure on the upstream side to achieve a specific flow of deionized water with a specific ion concentration, a perforated graphene sheet may require 8 PSI for the same flow rate the following.
如所述的那样,图2的石墨烯片212(或相当于图3的石墨烯片310)的穿孔312可以被功能化以有效阻止某一电荷的离子使其不通过该石墨烯片。如进一步所述的那样,还可以有效阻止与所述某一电荷相反电荷的离子,因为相反电荷的离子在不存在大量能量输入的情况下趋于与被阻止的某一电荷的离子一起滞留。因此,不预期经过石墨烯片的任何离子可以预期在石墨烯片-支撑室214的上游侧226中积聚。在上游“室”226中的离子积聚物本文称为“浓缩物”,并且最终降低水通过穿孔的石墨烯片212的流动,由此趋于使其不能有效地去离子化。如图2所示,提供其他路径230连同排出阀232以允许清除或排出该浓缩物。As mentioned, the perforations 312 of the graphene sheet 212 of FIG. 2 (or equivalently the graphene sheet 310 of FIG. 3 ) can be functionalized to effectively block ions of a certain charge from passing through the graphene sheet. As further described, ions of opposite charge to said one charge can also be efficiently blocked, since oppositely charged ions tend to stay together with the blocked one charge ion in the absence of substantial energy input. Therefore, any ions not expected to pass through the graphene sheet may be expected to accumulate in the upstream side 226 of the graphene sheet-support chamber 214 . The accumulation of ions in the upstream "chamber" 226 is referred to herein as a "concentrate" and ultimately reduces the flow of water through the perforated graphene sheet 212, thereby tending to make it less effective for deionization. As shown in FIG. 2 , an additional path 230 is provided along with a drain valve 232 to allow the concentrate to be purged or drained.
图2的装置或布置方案200的操作可以是“分批”方式。分批操作的第一方式随负载有离子的水通过路径210的流动而发生,并且排出阀232被关闭以防止流动。负载有离子的水填充支撑室214的上游侧226。水分子被允许流动通过图2的穿孔的石墨烯片212,并通过背衬片220到达支撑室214的下游侧227。离子(带正电荷和带负电荷的)积聚在上游侧226,并且去离子水积聚在下游部分227,并可以通过路径222排放至捕获容器(例示为罐224)。水分子的流动可以持续,直至在上游室226中积聚了阀值水平的浓缩物。此时,可以使用排放阀232通过路径230来进行上游离子的清除。The operation of the device or arrangement 200 of Figure 2 may be in a "batch" fashion. The first mode of batch operation occurs with the flow of ion-laden water through path 210, and discharge valve 232 is closed to prevent flow. Ion-laden water fills the upstream side 226 of the support chamber 214 . Water molecules are allowed to flow through the perforated graphene sheet 212 of FIG. 2 and through the backing sheet 220 to the downstream side 227 of the support chamber 214 . Ions (both positively and negatively charged) accumulate on the upstream side 226 and deionized water accumulates on the downstream portion 227 and can be discharged via path 222 to a capture vessel (exemplified as tank 224 ). The flow of water molecules may continue until a threshold level of concentrate has accumulated in the upstream chamber 226 . At this time, upstream ions can be purged through path 230 using discharge valve 232 .
通过例示,图2的石墨烯片212中穿孔(孔隙)312的边缘可以被功能化以具有负电荷。这可以通过使用氧、氮、磷、硫、氟、氯、溴或碘来使边缘功能化而实现。或者,这可以通过使用具有整体负电荷的聚合物链或氨基酸链来使边缘功能化而实现。因此,溶液中的任何带负电荷的离子将被排斥以使其不通过孔隙312,并且会聚集在上游室226中。此外,溶液中的带正电荷的离子将被吸引以使其与聚集在上游室226中的带负电荷的离子一起停留,并且也将不通过孔隙312。去离子水将通过孔隙并聚集在下游室227中。可以通过所述的分批工艺来清除上游室中的带正电荷的离子和带负电荷的离子。在供替代的实施方案中,图2的石墨烯片212中穿孔(或孔隙)312的边缘可以被功能化以具有正电荷。这可以通过使用硼、氢、锂、镁或铝来使边缘功能化而实现。或者,这可以通过使用具有整体正电荷的聚合物链或氨基酸链来使边缘功能化而实现。因此,溶液中的任何带正电荷的离子将被排斥以使其不通过孔隙312,并且会聚集在上游室226中。此外,溶液中的带负电荷的离子将被吸引以使其与聚集在上游室226中的带正电荷的离子一起停留,并且也将不通过孔隙312。去离子水将通过孔隙并聚集在下游室227中。可以通过所述的分批工艺来清除上游室中的带正电荷的离子和带负电荷的离子。By way of example, the edges of the perforations (pores) 312 in the graphene sheet 212 of FIG. 2 can be functionalized to have a negative charge. This can be achieved by functionalizing the edges with oxygen, nitrogen, phosphorus, sulfur, fluorine, chlorine, bromine or iodine. Alternatively, this can be achieved by functionalizing the edges with polymer chains or amino acid chains with an overall negative charge. Accordingly, any negatively charged ions in the solution will be repelled from passing through the pores 312 and will collect in the upstream chamber 226 . Furthermore, the positively charged ions in solution will be attracted to stay with the negatively charged ions accumulated in the upstream chamber 226 and will not pass through the pores 312 as well. The deionized water will pass through the pores and collect in the downstream chamber 227 . The upstream chamber can be purged of positively and negatively charged ions by the batch process described. In an alternative embodiment, the edges of the perforations (or pores) 312 in the graphene sheet 212 of FIG. 2 may be functionalized to have a positive charge. This can be achieved by functionalizing the edges with boron, hydrogen, lithium, magnesium or aluminum. Alternatively, this can be achieved by functionalizing the edges with polymer chains or amino acid chains with an overall positive charge. Accordingly, any positively charged ions in the solution will be repelled from passing through the pores 312 and will collect in the upstream chamber 226 . Furthermore, the negatively charged ions in solution will be attracted to stay with the positively charged ions accumulated in the upstream chamber 226 and will not pass through the pores 312 as well. The deionized water will pass through the pores and collect in the downstream chamber 227 . The upstream chamber can be purged of positively and negatively charged ions by the batch process described.
除了经功能化以吸引或排斥某些离子的石墨烯片的孔隙之外,在实施方案中,孔隙还可以被限定尺寸或改变尺寸以不允许某一尺寸的离子通过。例如,可以由被限定尺寸以不允许或禁止氯离子流动的孔隙312来穿孔石墨烯片212;这些孔隙的标称直径为1.3nm至2nm。因此,如果限定孔隙的尺寸为1.3nm至2nm,则氯离子不能通过穿孔的石墨烯片212并停留在上游部分或室226中。(还通过边缘的功能化来排斥氯离子使其远离该孔隙)。在一些实施方案中,孔隙312的标称直径可以为0.8nm至1.2nm。此外,在溶液中的带正电荷的钠离子会受影响而与聚集在上游室226中的带负电荷的氯离子一起停留,并且也将不通过孔隙312。去离子水将经过孔隙并聚集在下游室227中。改变孔隙的尺寸以与功能化石墨烯片的边缘组合地过滤离子,这可以导致去离子化工艺的效率增加。使用具有不同孔隙尺寸的带电荷的石墨烯片进行去离子化的方法和系统的更详细的描述公开于同时待审的第12/868,150号美国专利申请(现在指定为第8,361,321号美国专利)中,通过参考方式将其全部并入本文中。In addition to the pores of the graphene sheet being functionalized to attract or repel certain ions, in embodiments the pores may also be sized or sized to not allow passage of ions of a certain size. For example, the graphene sheet 212 may be perforated by pores 312 sized to not allow or prohibit the flow of chloride ions; these pores have a nominal diameter of 1.3nm to 2nm. Therefore, if the size of the defined pores is 1.3nm to 2nm, chloride ions cannot pass through the perforated graphene sheet 212 and stay in the upstream portion or chamber 226 . (Also by functionalization of the edges to repel chloride ions away from the pore). In some embodiments, pores 312 may have a nominal diameter of 0.8 nm to 1.2 nm. Furthermore, the positively charged sodium ions in solution will be affected to stay with the negatively charged chloride ions accumulated in the upstream chamber 226 and will also not pass through the pores 312 . The deionized water will pass through the pores and collect in the downstream chamber 227 . Changing the size of the pores to filter ions in combination with the edges of the functionalized graphene sheets can lead to increased efficiency of the deionization process. A more detailed description of a method and system for deionization using charged graphene sheets with varying pore sizes is disclosed in co-pending U.S. Patent Application No. 12/868,150 (now designated U.S. Patent No. 8,361,321) , which is incorporated herein by reference in its entirety.
在另一实施方案中,除了经功能化以吸引或排斥某些离子的石墨烯片的孔隙之外,可以使整个石墨烯片带电荷,向该片增加带相似电荷的离子的排斥。例如,具有用诸如氧的带负电荷的离子功能化的孔隙的石墨烯片还可以与电压源连接,使得负电荷置于整个片上。具有负电荷的氯离子被排斥而不运送通过带负电荷的穿孔的石墨烯片212,并且停留在上游部分或室226中。此外,溶液中的带正电荷的钠离子将受影响而与聚集在上游室226中的带负电荷的氯离子一起停留,并且也将不通过孔隙312。去离子水将通过孔隙并聚集在下游室227中。In another embodiment, the entire graphene sheet can be charged except for the pores of the graphene sheet which are functionalized to attract or repel certain ions, adding repulsion of similarly charged ions to the sheet. For example, a graphene sheet with pores functionalized with negatively charged ions such as oxygen can also be connected to a voltage source such that negative charges are placed across the sheet. Negatively charged chloride ions are repelled from transport through the negatively charged perforated graphene sheet 212 and reside in the upstream portion or chamber 226 . Furthermore, the positively charged sodium ions in solution will be affected to stay with the negatively charged chloride ions accumulated in the upstream chamber 226 and will also not pass through the pores 312 . The deionized water will pass through the pores and collect in the downstream chamber 227 .
如所理解的,使用不同尺寸的孔隙并使石墨烯片带电荷的促进离子排斥的另外方法可以以不同方式与使用经功能化的孔隙相结合。因此,一个实施方案可以使用经功能化的孔隙和不同尺寸的孔隙,而另一实施方案可以使用经功能化的孔隙和带电荷的石墨烯片。又一实施方案可以同时使用所有三种方法,即,功能化、不同孔隙尺寸和带电荷的石墨烯片。As will be appreciated, the additional approach of promoting ion repulsion using pores of different sizes and charging the graphene sheets can be combined in various ways with the use of functionalized pores. Thus, one embodiment may use functionalized pores and pores of different sizes, while another embodiment may use functionalized pores and charged graphene sheets. Yet another embodiment can use all three approaches simultaneously, ie, functionalization, different pore sizes, and charged graphene sheets.
图4是具有多个穿孔(如图3的穿孔)的石墨烯片的图示。图4的片限定了20个孔隙312。原则上,流率与孔隙密度成比例。随着孔隙密度增加,通过孔隙的流动可以变成“湍流的”,这可能负面影响了在给定压力下的流动。此外,随着孔隙密度增加,可能局部降低了在下面的石墨烯片的强度。这样的强度降低在某些情形下可能导致膜的破裂。对于0.6纳米的孔隙,孔隙之间的中心间距在15纳米的值时被认为是近似最佳的。在图4的实施方案中,用氧功能化孔隙312的边缘,尽管如本文别处所述,可以用其他元素或用聚合物链或氨基酸链来使边缘带电荷。碳邻近于所示的氧功能化。4 is an illustration of a graphene sheet with a plurality of perforations, such as the perforations of FIG. 3 . The sheet of FIG. 4 defines twenty apertures 312 . In principle, the flow rate is proportional to the pore density. As the pore density increases, the flow through the pores can become "turbulent," which can negatively affect the flow at a given pressure. Furthermore, as the pore density increases, the strength of the underlying graphene sheet may be locally reduced. Such a reduction in strength may in some cases lead to rupture of the membrane. For pores of 0.6 nm, the center-to-center spacing between pores was found to be approximately optimal at a value of 15 nm. In the embodiment of FIG. 4, the edges of the pores 312 are functionalized with oxygen, although as described elsewhere herein, the edges may be charged with other elements or with polymer chains or amino acid chains. Carbons are functionalized adjacent to the oxygens shown.
图4中所示的孔隙在穿孔或孔隙的边缘周围功能化。在图4所示的实施方案中,使用氧、氮、磷、硫、氟、氯、溴或碘来功能化孔隙的边缘,这使得该边缘具有负电荷。在另一实施方案(未示出)中,使用硼、氢、锂、镁或铝来功能化孔隙的边缘,这使得该边缘具有正电荷。或者,可以使用聚合物链或氨基酸链来功能化孔隙的边缘,并且该边缘所具有的电荷取决于所用的具体的聚合物或氨基酸。The pores shown in Figure 4 are functionalized around the edges of the perforations or pores. In the embodiment shown in Figure 4, the edges of the pores are functionalized with oxygen, nitrogen, phosphorus, sulfur, fluorine, chlorine, bromine, or iodine, which renders the edges negatively charged. In another embodiment (not shown), the edges of the pores are functionalized with boron, hydrogen, lithium, magnesium, or aluminum, which renders the edges positively charged. Alternatively, polymer chains or amino acid chains can be used to functionalize the edges of the pores, and the charge of the edges depends on the particular polymer or amino acid used.
图5是可以与图2的石墨烯片一起使用的背衬片的结构的简化图。在图5中,背衬片220由聚四氟乙烯(还称为聚四氟乙烷)的细丝520制成,布置在矩形栅格中并在它们的交叉点处粘合或融合。如同穿孔的石墨烯片一样,对于最大流动,背衬片的尺寸应尽可能大,与足够的强度相称。朝向相同方向的相互邻近的细丝520之间的间距可以标称为100nm,并且细丝可以具有40nm的标称直径。石墨烯片的抗拉强度是大的,因此背衬片中相对大的未支撑的区域不应成为问题。5 is a simplified diagram of the structure of a backing sheet that may be used with the graphene sheet of FIG. 2 . In Figure 5, the backing sheet 220 is made of filaments 520 of polytetrafluoroethylene (also known as polytetrafluoroethylene), arranged in a rectangular grid and glued or fused at their intersections. As with perforated graphene sheets, for maximum flow, the size of the backing sheet should be as large as possible commensurate with sufficient strength. The spacing between mutually adjacent filaments 520 facing the same direction may be nominally 100 nm, and the filaments may have a nominal diameter of 40 nm. The tensile strength of the graphene sheet is large, so relatively large unsupported areas in the backing sheet should not be a problem.
图6是本公开的另一实施方案或另一方面的去离子化或脱盐装置600(即,溶液去离子器)的抽象图示,其中使用多层的不同功能化的石墨烯片。在图6中,与图2的部件相对应的部件由相似的参考字母数字指定。在图6的支撑室614内,上游和下游穿孔的石墨烯片612a和612b分别将该室分成三个容积或部分,即,上游部分或室626a、下游部分或室627a、以及中间部分或室629。如本文所用,术语上游和下游是按照装置中水的流动,表达该装置的部件相对于其他部件的关系,所述水的流动从输入通道210到达第一石墨烯片612a,然后从第一石墨烯片612a到达第二石墨烯片612b,然后从第二石墨烯片到达输出通道222。因此,尽管穿孔的石墨烯片612a相对于下游石墨烯片612b处于上游,但穿孔的石墨烯片612a相对于输入通道210处于下游。显著地,术语下游不旨在必须意指部件之间的高度关系,即,尽管第二石墨烯片612b可以处于第一石墨烯片612a的下游,但这未必表示第二石墨烯片612b比第一石墨烯片612a高度更低,尽管其可以如此。如所理解的,可以加压该装置,从而下游部件可以依据流动而处于下游,但可以处于比上游部件更高的高度。6 is an abstract illustration of another embodiment or aspect of the present disclosure of a deionization or desalination device 600 (ie, a solution deionizer) in which multiple layers of differently functionalized graphene sheets are used. In FIG. 6, components corresponding to those of FIG. 2 are designated by like reference alphanumerics. Within the support chamber 614 of FIG. 6, upstream and downstream perforated graphene sheets 612a and 612b, respectively, divide the chamber into three volumes or sections, namely, an upstream section or chamber 626a, a downstream section or chamber 627a, and an intermediate section or chamber. 629. As used herein, the terms upstream and downstream are in terms of the flow of water in the device, expressing the relationship of the components of the device relative to other components, from the input channel 210 to the first graphene sheet 612a, and then from the first graphite The ene sheet 612a goes to the second graphene sheet 612b , and from the second graphene sheet to the output channel 222 . Thus, while perforated graphene sheet 612a is upstream relative to downstream graphene sheet 612b , perforated graphene sheet 612a is downstream relative to input channel 210 . Significantly, the term downstream is not intended to necessarily imply a height relationship between components, i.e., although the second graphene sheet 612b may be downstream of the first graphene sheet 612a, this does not necessarily mean that the second graphene sheet 612b is more downstream than the first graphene sheet 612a. A graphene sheet 612a is lower in height, although it could be. As will be appreciated, the device may be pressurized so that downstream components may be downstream in terms of flow, but may be at a higher elevation than upstream components.
具体地,图6的溶液或水去离子器装置具有从水201、从器皿或容器216或泵218至通道210的溶液流动路径,通道210可以被认为是溶液流动路径的输入端。从通道210,溶液流动路径延伸至室614的上游室626a,通过石墨烯片612a,通过中间室629,通过石墨烯片612b,然后到达下游室627a,最终到达通道222,通道222可以被认为是溶液流动路径的输入端。Specifically, the solution or water deionizer device of FIG. 6 has a solution flow path from water 201 , from a vessel or container 216 or pump 218 to a channel 210 which may be considered the input of the solution flow path. From channel 210, the solution flow path extends to upstream chamber 626a of chamber 614, through graphene sheet 612a, through intermediate chamber 629, through graphene sheet 612b, then to downstream chamber 627a, and finally to channel 222, which may be considered as The input end of the solution flow path.
每一穿孔的石墨烯片612a和612b伴随有背衬片。更具体地,由片620a支持穿孔的石墨烯片612a,并且由片620b支持穿孔的石墨烯片612b。如所指出的,石墨烯是单原子层厚的碳原子层,其结合在一起限定了片310,如图3所例示。还如所指出的,可以通过向该片施用背衬结构来改善石墨烯片的弯曲。Each perforated graphene sheet 612a and 612b is accompanied by a backing sheet. More specifically, perforated graphene sheet 612a is supported by sheet 620a, and perforated graphene sheet 612b is supported by sheet 620b. As noted, graphene is a monoatomic layer thick layer of carbon atoms that bond together to define a sheet 310 , as illustrated in FIG. 3 . As also noted, the bending of graphene sheets can be improved by applying a backing structure to the sheet.
更特别地,在实施方案中,用孔隙612ac的带负电荷的边缘功能化上游石墨烯片612a以排斥氯离子使其不通过该孔隙。具有负电荷的氯离子可以被排斥而不经过石墨烯片612a的带负电荷的边缘,由此停留在室626a的上游部分中。然而,如所理解的,在片612a的输入侧上存在被排斥的氯离子将影响钠离子,使其也停留在输入侧上。如所指出的,氯离子和钠离子的分离将需要大量的能量输入系统内,这不是本发明的特征。因此,通过排斥氯离子使其不通过石墨烯片,也可有效地排斥钠离子使其不通过上游石墨烯片。More specifically, in an embodiment, the upstream graphene sheet 612a is functionalized with the negatively charged edges of the pores 612ac to repel chloride ions from passing through the pores. Negatively charged chloride ions may be repelled from passing the negatively charged edge of the graphene sheet 612a, thereby staying in the upstream portion of the chamber 626a. However, as will be appreciated, the presence of repelled chloride ions on the input side of sheet 612a will affect the sodium ions to stay on the input side as well. As noted, the separation of chloride and sodium ions would require significant energy input into the system, which is not a feature of the present invention. Thus, by repelling chloride ions from passing through the graphene sheet, sodium ions are also effectively repelled from passing through the upstream graphene sheet.
可能存在如下情形,其中一些钠离子可以仍然通过上游石墨烯片的孔隙。例如,如果输入溶液具有相对于氯离子的过量的钠离子时,则过量的钠离子可以被石墨烯片上的负电荷所吸引而通过该孔隙。在另一实例中,输入溶液可以包含带正电荷的且不为钠的第三离子,其可以被吸引而运送通过上游石墨烯片孔隙。在这些情形中,可以期望具有第二石墨烯片以过滤离子。此外,可以期望具有第二石墨烯片以确保更高水平的脱盐。There may be situations where some sodium ions may still pass through the pores of the upstream graphene sheet. For example, if the input solution has an excess of sodium ions relative to chloride ions, the excess sodium ions can be attracted by the negative charges on the graphene sheet to pass through the pores. In another example, the input solution may contain a positively charged third ion other than sodium that may be attracted to transport through the pores of the upstream graphene sheet. In these cases it may be desirable to have a second graphene sheet to filter ions. Furthermore, it may be desirable to have a second graphene sheet to ensure higher levels of desalination.
因此,图6的实施方案包括下游石墨烯片612b,其经穿孔而具有孔隙612bs(第二孔隙)并可以带正电荷以排斥钠离子(或任何其他带正电荷的离子)运送通过石墨烯片612b。如果钠或其他正离子能够运送通过片612a而进入室629,则其可以被排斥而不运送通过下游带正电荷的穿孔的石墨烯片612b,因此停留或积聚在中间部分或室629中。此外,以任何氯离子能运送进入室629的程度来说,那些氯离子可以被吸引以与629中的钠离子一起滞留,并且也不会运送通过片612b。因此,至少基本不含氯离子和钠离子的水分子(H2O)可以从中间部分或室629流动通过穿孔的石墨烯片612b的孔隙612bs并进入下游部分或室627a,从此处可以通过水流动路径222和收集器皿224收集去离子水。水流动路径222可以被认为是水流动路径输出端,并且阀(未示出)可以用作水流动路径输出端222上的水流动路径输出阀。如所理解的,可以类似地操作可供替代的实施方案,其中上游石墨烯片612a具有带正电荷的孔隙以及下游石墨烯片612b具有带负电荷的孔隙。Thus, the embodiment of FIG. 6 includes a downstream graphene sheet 612b that is perforated to have pores 612bs (second pores) and can be positively charged to repel the transport of sodium ions (or any other positively charged ions) through the graphene sheet. 612b. If sodium or other positive ions are able to transport through the sheet 612a into the chamber 629, they may be repelled from being transported through the downstream positively charged perforated graphene sheet 612b, thus staying or accumulating in the middle portion or chamber 629. Furthermore, to the extent that any chloride ions can be transported into chamber 629, those chloride ions may be attracted to stay with the sodium ions in 629 and also not transported through sheet 612b. Thus, water molecules (H 2 O) at least substantially free of chloride and sodium ions can flow from the middle portion or chamber 629 through the pores 612bs of the perforated graphene sheet 612b and into the downstream portion or chamber 627a, from where water can pass through. Flow path 222 and collection vessel 224 collect deionized water. Water flow path 222 may be considered a water flow path output, and a valve (not shown) may serve as a water flow path output valve on water flow path output 222 . As will be appreciated, an alternative embodiment in which the upstream graphene sheet 612a has positively charged pores and the downstream graphene sheet 612b has negatively charged pores can operate similarly.
因此,尽管预期图2中所示的单石墨烯片去离子器可以(若经适当“调整”)足以生产去离子水,图6中所示的两石墨烯片去离子器提供了能够满足最高去离子化标准的额外的层。如所理解的,第二石墨烯片可以替代地被功能化以排斥不同类型的离子。此外,采用多于两个石墨烯片的系统可以用于确保过滤不同类型的离子并确保去离子水满足最高标准。Thus, while it is expected that the single graphene sheet deionizer shown in Figure 2 could (if properly "tuned") adequately produce deionized water, the two graphene sheet deionizer shown in Figure 6 provides the ability to meet the highest Additional layer of deionization standard. As will be appreciated, the second graphene sheet may alternatively be functionalized to repel different types of ions. Additionally, systems employing more than two graphene sheets can be used to ensure that different types of ions are filtered and that deionized water meets the highest standards.
如同图2的去离子化布置方案200的情况,图6的装置或布置方案600在去离子化操作期间积聚或浓缩离子。更具体地,对于负载有氯离子和钠离子的水流,预期大部分氯离子和钠离子会被上游石墨烯片612a所排斥,导致装置600的上游部分或室626a积聚具有氯离子和钠离子的浓缩物。中间部分或室629也积聚了一定浓度的氯离子和钠离子,尽管预期该浓度远低于在上游室中积聚的浓度。可以分别通过选择性控制清除连接件630a和630b及其清除阀632a和632b来分别提取这些浓缩的离子。更具体地,可以打开阀632a以使浓缩的氯离子和钠离子从上游部分或室626a流动至例示为罐634a的收集器皿,并且可以打开阀632b以使浓缩的氯离子和钠离子从中间部分或室629流动至例示为罐634b的收集器皿。理想地,在开始清除中间部分或罐629之前关闭清除阀632a,从而在整个穿孔的石墨烯片612a上保持一定压力以提供水通过穿孔的石墨烯片612a的流动,从而帮助从中间室629冲洗富集钠离子的浓缩物。在进行去离子化之前关闭清除阀632a和632b。对于在钠的情况下转化成固体形式或在氯的情况下转化成气体形式而言,清除并收集的浓缩的离子可能具有经济价值。应注意海水含有大量的铍盐,并且这些盐如果优先被浓缩,则作为催化剂对制药工业具有价值。如所理解的,可以类似地操作可供替代的实施方案,其中用孔隙612ac的带正电荷的边缘功能化上游石墨烯片612a并用带负电荷的边缘612bs功能化下游石墨烯片612b,并且大部分离子积聚在上游室626a中且远远更低浓度的离子积聚在中间室629中。那些积聚的离子可以如上所述被清除。As was the case with the deionization arrangement 200 of Figure 2, the device or arrangement 600 of Figure 6 accumulates or concentrates ions during a deionization operation. More specifically, for a water stream laden with chloride and sodium ions, it is expected that the majority of the chloride and sodium ions would be repelled by the upstream graphene sheet 612a, causing the upstream portion or chamber 626a of the device 600 to accumulate chlorine and sodium ions. concentrate. The middle portion or chamber 629 also accumulates some concentration of chloride and sodium ions, although this concentration is expected to be much lower than that accumulated in the upstream chamber. These concentrated ions can be extracted by selective control of purge connections 630a and 630b and their purge valves 632a and 632b, respectively. More specifically, valve 632a can be opened to allow concentrated chloride and sodium ions to flow from the upstream portion or chamber 626a to a collection vessel, illustrated as tank 634a, and valve 632b can be opened to allow concentrated chloride and sodium ions to flow from the intermediate portion. OR chamber 629 flows to a collection vessel, illustrated as tank 634b. Ideally, the purge valve 632a is closed before beginning to purge the midsection or tank 629, thereby maintaining some pressure across the perforated graphene sheet 612a to provide flow of water through the perforated graphene sheet 612a to aid flushing from the midchamber 629 Concentrate rich in sodium ions. Purge valves 632a and 632b are closed prior to deionization. The scavenged and collected concentrated ions may be of economic value for conversion to solid form in the case of sodium or to gaseous form in the case of chlorine. It should be noted that seawater contains significant amounts of beryllium salts, and these salts, if preferentially concentrated, could be valuable to the pharmaceutical industry as catalysts. As will be appreciated, an alternative embodiment in which the upstream graphene sheet 612a is functionalized with the positively charged edges of the aperture 612ac and the downstream graphene sheet 612b is functionalized with the negatively charged edges 612bs can be operated similarly, and large Part of the ions accumulates in the upstream chamber 626 a and a much lower concentration of ions accumulates in the intermediate chamber 629 . Those accumulated ions can be removed as described above.
图6还例示出交叉流动阀654a和654b,其分别连通了流动路径658和上游部分或室626a以及流动路径658和中间部分或室629。负载有离子的未过滤的水201可以通过打开阀652而按照路线运送至流动路径658,或者可以通过操作泵660而由罐224提供去离子水202。从泵660,去离子通过止回阀656流动至路径658。交叉流动阀654a和654b分别与清除阀632a和632b同时打开和关闭,由此帮助从室中清除浓缩物。Figure 6 also illustrates cross flow valves 654a and 654b, which communicate flow path 658 with upstream portion or chamber 626a and flow path 658 with intermediate portion or chamber 629, respectively. Ion-laden unfiltered water 201 may be routed to flow path 658 by opening valve 652 , or deionized water 202 may be provided by tank 224 by operating pump 660 . From pump 660 , deionization flows through check valve 656 to path 658 . Cross flow valves 654a and 654b are opened and closed simultaneously with purge valves 632a and 632b, respectively, thereby helping to purge concentrate from the chamber.
如所讨论的,除了将石墨烯片的孔隙功能化以排斥某些离子之外,去离子器中的石墨烯片还可以被限定尺寸以不允许某一尺寸的离子通过或运送。例如,可以改变穿孔的尺寸以通过选择约1.3nm至2nm的孔隙尺寸而不允许氯离子通过。或者,可以改变穿孔的尺寸以通过选择约1.3纳米的孔隙尺寸而不允许钠离子通过。改变孔隙的尺寸以过滤离子与功能化石墨烯片的孔隙相结合可以导致去离子化工艺的效率增加。As discussed, in addition to functionalizing the pores of the graphene sheets to repel certain ions, the graphene sheets in the deionizer can also be sized to not allow passage or transport of ions of a certain size. For example, the size of the perforations can be varied to not allow the passage of chloride ions by selecting a pore size of about 1.3 nm to 2 nm. Alternatively, the size of the perforations can be varied to not allow the passage of sodium ions by selecting a pore size of about 1.3 nanometers. Changing the size of the pores to filter ions combined with the pores of functionalized graphene sheets can lead to increased efficiency of the deionization process.
在实施方案中,在石墨烯片612a和612b上的穿孔的尺寸在尺寸方面不同,从而一个片有效地不允许负载有氯的水流动,并且一个片有效地不允许负载有钠的水流动。在包括不同尺寸的穿孔以及孔隙的功能化的实施方案中,通过这二者来实现去离子化。通过例示,由经限定尺寸以不允许或禁止氯离子流动的孔隙612ac穿孔上游石墨烯片612a;这些孔隙的标称直径为1.3nm至2nm。因此,氯离子不能经过穿孔的石墨烯片612a,而停留在上游部分或室626a中。也间接地排斥钠离子使其不能通过穿孔的石墨烯片612a流入中间室629,因为钠离子将趋于与被排斥的氯离子一起滞留以防止电荷积累。使用经限定尺寸以不允许或禁止钠离子流动的孔隙612bs穿孔下游穿孔的石墨烯片612b;这些孔隙的标称直径为1.3纳米。至少不含氯离子和钠离子的水分子(H2O)可以从中间部分或室629流经穿孔的石墨烯片612b的孔隙612bs而进入下游部分或室627a,从此处可以通过路径222和收集器皿224来收集去离子水。In an embodiment, the size of the perforations on the graphene sheets 612a and 612b differ in size such that one sheet effectively does not allow flow of chlorine laden water and one sheet effectively does not allow flow of sodium laden water. In embodiments that include perforations of different sizes and functionalization of the pores, deionization is achieved through both. By way of illustration, the upstream graphene sheet 612a is perforated by pores 612ac sized to allow or prohibit the flow of chloride ions; these pores have a nominal diameter of 1.3nm to 2nm. Thus, chloride ions cannot pass through the perforated graphene sheet 612a, but remain in the upstream portion or chamber 626a. Sodium ions are also indirectly repelled from flowing through the perforated graphene sheet 612a into the intermediate chamber 629, since the sodium ions will tend to stay with the repelled chloride ions to prevent charge buildup. The downstream perforated graphene sheet 612b is perforated with pores 612bs sized to allow or prohibit the flow of sodium ions; these pores have a nominal diameter of 1.3 nanometers. Water molecules (H 2 O) free of at least chloride and sodium ions can flow from the middle portion or chamber 629 through the pores 612bs of the perforated graphene sheet 612b and into the downstream portion or chamber 627a, from where they can pass through the pathway 222 and collect Vessel 224 to collect deionized water.
还如关于去离子器所讨论的,除了将石墨烯片的孔隙功能化以吸引或排斥某些离子之外,可以向每一石墨烯片应用电荷,增加每一石墨烯片对带相反电荷的离子的吸引和对带相似电荷的离子的排斥。例如,除了具有经功能化的孔隙之外,上游石墨烯片612a可以带负电荷,这导致其排斥氯离子使其不通过孔隙612ac。具有负电荷的氯离子停留在上游部分或室626a中,因为其被经功能化的孔隙612ac和片612a上的负电荷所排斥。此外,带正电荷的钠离子也将趋于与氯离子一起停留在上游室626a中。尽管相当高浓度的氯离子和钠离子将被功能化和石墨烯片612a的电荷所排斥(直接或间接地),但是如关于仅具有经功能化的孔隙的实施方案所指出的,可能的是,一些氯、钠或其他离子仍可以通过孔隙612ac。如发生该情形,用孔隙612bs穿孔下游穿孔的石墨烯片612b,并且除了具有正功能化的孔隙之外,石墨烯片612b还带有正电荷。这种正电荷排斥钠离子运送通过石墨烯片612b,并且还间接地排斥可能到达中间室629的任何氯离子的运送。至少不含氯离子和钠离子的水分子(H2O)(去离子水)可以从中间部分或室629流经穿孔的石墨烯片612b的孔隙612bs而进入下游部分或室627a,从此处可以通过路径222和收集器皿224来收集去离子水。类似地操作可供替代的实施方案,其中向上游石墨烯片612a(其中片612a还具有带正电荷的经功能化的孔隙612ac)应用正电荷并且向下游石墨烯片612b(其中片612b还具有带负电荷的经功能化的孔隙612bs)应用负电荷。Also as discussed with respect to the deionizer, in addition to functionalizing the pores of the graphene sheets to attract or repel certain ions, an electric charge can be applied to each graphene sheet, increasing the pair of oppositely charged Attraction of ions and repulsion of similarly charged ions. For example, in addition to having functionalized pores, upstream graphene sheet 612a may be negatively charged, causing it to repel chloride ions from passing through pores 612ac. Negatively charged chloride ions stay in the upstream portion or chamber 626a because they are repelled by the functionalized pores 612ac and the negative charge on the sheet 612a. In addition, the positively charged sodium ions will also tend to stay with the chloride ions in the upstream chamber 626a. Although relatively high concentrations of chloride and sodium ions will be repelled (directly or indirectly) by the functionalization and charge of the graphene sheet 612a, as noted for embodiments with only functionalized pores, it is possible , some chlorine, sodium or other ions can still pass through the pores 612ac. If this occurs, the downstream perforated graphene sheet 612b is perforated with apertures 612bs, and in addition to having positively functionalized apertures, the graphene sheet 612b also carries a positive charge. This positive charge repels the transport of sodium ions through the graphene sheet 612b and also indirectly repels the transport of any chloride ions that might reach the intermediate chamber 629 . Water molecules (H 2 O) (deionized water) free of at least chloride and sodium ions can flow from the middle portion or chamber 629 through the pores 612bs of the perforated graphene sheet 612b and into the downstream portion or chamber 627a, from where The deionized water is collected through path 222 and collection vessel 224 . An alternative embodiment is operated similarly, where a positive charge is applied to the upstream graphene sheet 612a (where the sheet 612a also has positively charged functionalized pores 612ac) and to the downstream graphene sheet 612b (where the sheet 612b also has positively charged functionalized pores 612ac). Negatively charged functionalized pores 612bs) apply a negative charge.
如所理解的,使用不同尺寸的孔隙并使石墨烯片带电荷的另外的离子排斥方法可以以不同方式与使用经功能化的孔隙相结合。因此,一个实施方案可以使用经功能化的孔隙和不同尺寸的孔隙,而另一实施方案可以使用经功能化的孔隙和带电荷的石墨烯片。又一实施方案可以同时使用所有三种方法,即,功能化、不同孔隙尺寸和带电荷的石墨烯片。As will be appreciated, additional ion repulsion methods using pores of different sizes and charging the graphene sheets can be combined in various ways with the use of functionalized pores. Thus, one embodiment may use functionalized pores and pores of different sizes, while another embodiment may use functionalized pores and charged graphene sheets. Yet another embodiment can use all three approaches simultaneously, ie, functionalization, different pore sizes, and charged graphene sheets.
图7是根据本公开一方面的去离子化布置方案的简化图。与图6部件相对应的图7部件用相似的参考字母数字指定。在图7中,将穿孔的石墨烯片612a和612b卷起或螺旋缠绕成圆柱体形式,并且插入外壳(分别例示为712a和712b),如RO膜领域中所已知的。7 is a simplified diagram of a deionization arrangement according to an aspect of the present disclosure. Components of FIG. 7 that correspond to components of FIG. 6 are designated with like reference alphanumerics. In FIG. 7, perforated graphene sheets 612a and 612b are rolled or helically wound into a cylindrical form and inserted into a housing (illustrated as 712a and 712b, respectively), as is known in the art of RO membranes.
本领域技术人员会理解,通过一个石墨烯片或多个石墨烯片上的孔隙的选择性功能化,可以从水中除去除氯和钠之外的其它离子。Those skilled in the art will appreciate that ions other than chlorine and sodium can be removed from water by selective functionalization of pores on a graphene sheet or sheets.
用于使水溶液去离子化的方法包括以下步骤:使石墨烯片的多个孔隙功能化以排斥所述溶液中的第一离子使其不运送通过所述经功能化的多个孔隙,未被传送的第一离子影响所述溶液中的第二离子以使其未运送通过所述经功能化的多个孔隙;将所述石墨烯片置于溶液流动路径输入端和溶液流动路径输出端之间;以及使溶液进入所述溶液流动路径输入端并通过所述石墨烯片的经功能化的多个孔隙,由此产生在所述石墨烯片的溶液流动路径输出侧上的去离子化的溶液以及在所述石墨烯片的溶液流动路径输入侧上的包含第一离子和第二离子的第二溶液。The method for deionizing an aqueous solution comprises the steps of: functionalizing a plurality of pores of a graphene sheet to repel first ions in the solution from being transported through the functionalized plurality of pores, which are not transporting a first ion to affect a second ion in the solution so that it is not transported through the functionalized plurality of pores; placing the graphene sheet between a solution flow path input and a solution flow path output and passing a solution into the solution flow path input end and through the functionalized plurality of pores of the graphene sheet, thereby creating a deionized on the solution flow path output side of the graphene sheet solution and a second solution comprising first ions and second ions on the input side of the solution flow path of the graphene sheet.
用于使溶液去离子化的方法包括以下步骤:使第一石墨烯片的第一多个孔隙功能化以排斥所述溶液中的第一离子而使其不运送通过所述经功能化的第一多个孔隙,未被运送的第一离子还影响所述溶液中的第二离子而使其不运送通过所述经功能化的第一多个孔隙;使第二石墨烯片的第二多个孔隙功能化以排斥所述溶液中的第二离子,未被运送的第二离子还影响所述溶液中的第一离子而使其不运送通过所述经功能化的第二多个孔隙;将所述第一石墨烯片置于溶液流动路径输入端的下游并且将所述第二石墨烯片置于所述第一石墨烯片和溶液流动输出端之间;以及使溶液进入所述溶液流动路径输入端,通过所述第一石墨烯片,然后通过所述第二石墨烯片,由此在所述溶液流动路径输出端处产生去离子化的溶液。The method for deionizing a solution comprises the step of: functionalizing a first plurality of pores of a first graphene sheet to repel first ions in the solution from transport through the functionalized first ions. a plurality of pores, the untransported first ions also affect second ions in the solution from being transported through the functionalized first plurality of pores; making the second plurality of pores of the second graphene sheet one of the pores is functionalized to repel second ions in the solution, the non-transported second ions also affecting the first ions in the solution from being transported through the functionalized second plurality of pores; placing the first graphene sheet downstream of the solution flow path input and placing the second graphene sheet between the first graphene sheet and the solution flow output; and passing solution into the solution flow A path input, through the first graphene sheet, and then through the second graphene sheet, thereby producing a deionized solution at the solution flow path output.
Claims (36)
Applications Claiming Priority (3)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| US13/422,753 US20130240355A1 (en) | 2012-03-16 | 2012-03-16 | Functionalization of graphene holes for deionization |
| US13/422,753 | 2012-03-16 | ||
| PCT/US2013/029361 WO2013138137A1 (en) | 2012-03-16 | 2013-03-06 | Functionalization of graphene holes for deionization |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN104203835A true CN104203835A (en) | 2014-12-10 |
Family
ID=47884618
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201380014413.9A Pending CN104203835A (en) | 2012-03-16 | 2013-03-06 | Functionalization of graphene holes for deionization |
Country Status (12)
| Country | Link |
|---|---|
| US (1) | US20130240355A1 (en) |
| EP (1) | EP2825507A1 (en) |
| JP (1) | JP2015516286A (en) |
| KR (1) | KR20140138963A (en) |
| CN (1) | CN104203835A (en) |
| AU (1) | AU2013232453A1 (en) |
| CA (1) | CA2864727A1 (en) |
| IL (1) | IL234610A0 (en) |
| IN (1) | IN2014DN07265A (en) |
| SA (1) | SA113340389B1 (en) |
| SG (2) | SG10201607771VA (en) |
| WO (1) | WO2013138137A1 (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN108219397A (en) * | 2017-12-27 | 2018-06-29 | 复旦大学 | A kind of method for improving polyethylene terephthalate crystalline rate |
| CN110869109A (en) * | 2017-07-14 | 2020-03-06 | 国立大学法人信州大学 | Nano-window structure of graphene and method for manufacturing high-purity gas |
| CN114901591A (en) * | 2020-03-05 | 2022-08-12 | 寿控股有限公司 | Carbon material and method for producing carbon material |
Families Citing this family (42)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US9475709B2 (en) | 2010-08-25 | 2016-10-25 | Lockheed Martin Corporation | Perforated graphene deionization or desalination |
| US9193587B2 (en) | 2011-07-13 | 2015-11-24 | Lockheed Martin Corporation | System and method for water purification and desalination |
| AR082603A1 (en) | 2011-08-09 | 2012-12-19 | Lavaque Oscar | A CARBON DIOXIDE SOLUBILIZING DEVICE IN A VARIABLE PRESSURE DRINK |
| AU2013235643B2 (en) | 2012-03-21 | 2015-12-17 | Lockheed Martin Corporation | Methods for perforating graphene using an activated gas stream and perforated graphene produced therefrom |
| US9463421B2 (en) | 2012-03-29 | 2016-10-11 | Lockheed Martin Corporation | Planar filtration and selective isolation and recovery device |
| US9095823B2 (en) * | 2012-03-29 | 2015-08-04 | Lockheed Martin Corporation | Tunable layered membrane configuration for filtration and selective isolation and recovery devices |
| US9067811B1 (en) * | 2012-05-25 | 2015-06-30 | Lockheed Martin Corporation | System, method, and control for graphenoid desalination |
| US9610546B2 (en) | 2014-03-12 | 2017-04-04 | Lockheed Martin Corporation | Separation membranes formed from perforated graphene and methods for use thereof |
| US10213746B2 (en) | 2016-04-14 | 2019-02-26 | Lockheed Martin Corporation | Selective interfacial mitigation of graphene defects |
| US10653824B2 (en) | 2012-05-25 | 2020-05-19 | Lockheed Martin Corporation | Two-dimensional materials and uses thereof |
| US10980919B2 (en) | 2016-04-14 | 2021-04-20 | Lockheed Martin Corporation | Methods for in vivo and in vitro use of graphene and other two-dimensional materials |
| US9834809B2 (en) | 2014-02-28 | 2017-12-05 | Lockheed Martin Corporation | Syringe for obtaining nano-sized materials for selective assays and related methods of use |
| US9744617B2 (en) | 2014-01-31 | 2017-08-29 | Lockheed Martin Corporation | Methods for perforating multi-layer graphene through ion bombardment |
| US9815557B2 (en) * | 2012-09-20 | 2017-11-14 | Humbay Health, LLC | Aircraft humidifier |
| CA2895088A1 (en) * | 2012-12-19 | 2014-06-26 | Lockheed Martin Corporation | Perforated graphene deionization or desalination |
| US9592475B2 (en) | 2013-03-12 | 2017-03-14 | Lockheed Martin Corporation | Method for forming perforated graphene with uniform aperture size |
| WO2014159043A1 (en) | 2013-03-13 | 2014-10-02 | Lockheed Martin Corporation | Nanoporous membranes and methods for making the same |
| US9480952B2 (en) | 2013-03-14 | 2016-11-01 | Lockheed Martin Corporation | Methods for chemical reaction perforation of atomically thin materials |
| US9572918B2 (en) | 2013-06-21 | 2017-02-21 | Lockheed Martin Corporation | Graphene-based filter for isolating a substance from blood |
| US20150014853A1 (en) * | 2013-07-09 | 2015-01-15 | Harper Laboratories, LLC | Semiconductor devices comprising edge doped graphene and methods of making the same |
| US9157159B2 (en) * | 2013-11-17 | 2015-10-13 | Don Lee Hansen | System and method for generating hydrogen and oxygen gases |
| JP2017507044A (en) | 2014-01-31 | 2017-03-16 | ロッキード マーティン コーポレイションLockheed Martin Corporation | Method for forming composite structures with two-dimensional materials using porous non-sacrificial support layers |
| WO2015116946A1 (en) | 2014-01-31 | 2015-08-06 | Lockheed Martin Corporation | Perforating two-dimensional materials using broad ion field |
| JP2017512129A (en) | 2014-03-12 | 2017-05-18 | ロッキード・マーチン・コーポレーション | Separation membranes formed from perforated graphene |
| CA2947029A1 (en) * | 2014-05-01 | 2015-11-05 | Lockheed Martin Corporation | Separation and assay of target entities using filtration membranes comprising a perforated two-dimensional material |
| CN107073408A (en) | 2014-09-02 | 2017-08-18 | 洛克希德马丁公司 | Hemodialysis membrane and blood filtration membrane based on two-dimensional membrane material and application method thereof |
| CA2994549A1 (en) | 2015-08-05 | 2017-02-09 | Lockheed Martin Corporation | Perforatable sheets of graphene-based material |
| WO2017023380A1 (en) | 2015-08-05 | 2017-02-09 | Lockheed Martin Corporation | Two-dimensional materials and uses thereof |
| CA2994664A1 (en) | 2015-08-06 | 2017-02-09 | Lockheed Martin Corporation | Nanoparticle modification and perforation of graphene |
| JP6362582B2 (en) * | 2015-11-30 | 2018-07-25 | コリア インスティチュート オブ エナジー リサーチ | Porous graphene member, method for producing porous graphene member, and apparatus for producing porous graphene member using the same |
| JP6054499B1 (en) * | 2015-11-30 | 2016-12-27 | コリア インスティチュート オブ エナジー リサーチ | Porous graphene filter manufacturing method, porous graphene filter manufactured using the same, and filter device using the same |
| US9981212B2 (en) | 2015-11-30 | 2018-05-29 | Korea Institute Of Energy Research | Method for manufacturing porous graphene filter, porous graphene filter manufactured using same, and filter apparatus using porous graphene filter |
| US9834445B2 (en) | 2015-11-30 | 2017-12-05 | Korea Institute Of Energy Research | Porous graphene member, method for manufacturing same, and apparatus for manufacturing same using the method |
| US20170194656A1 (en) * | 2015-12-30 | 2017-07-06 | Lockheed Martin Corporation | Perforated 2d flow battery separators |
| WO2017180135A1 (en) | 2016-04-14 | 2017-10-19 | Lockheed Martin Corporation | Membranes with tunable selectivity |
| KR20190019907A (en) | 2016-04-14 | 2019-02-27 | 록히드 마틴 코포레이션 | Handling graphene sheets for large-scale transport using the free-floating method |
| SG11201808961QA (en) | 2016-04-14 | 2018-11-29 | Lockheed Corp | Methods for in situ monitoring and control of defect formation or healing |
| JP2019517909A (en) | 2016-04-14 | 2019-06-27 | ロッキード・マーチン・コーポレーション | Two-dimensional membrane structure having a flow path |
| EP3506999A1 (en) * | 2016-09-05 | 2019-07-10 | Drei Lilien PVG GmbH & Co. KG | Open-pore membrane having an inner space-spanning polymeric structural network for electrophoretic material-selective separation and methods for producing and using same |
| CN107261857B (en) * | 2017-05-10 | 2020-06-30 | 四川大学 | Modified graphene membrane for separation of monovalent and multivalent metal ions and preparation method thereof |
| JP7095858B2 (en) * | 2018-01-11 | 2022-07-05 | 株式会社寿ホールディングス | Filter unit |
| JP7133429B2 (en) * | 2018-10-19 | 2022-09-08 | 日東電工株式会社 | Water treatment system and water treatment method |
Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US20100105834A1 (en) * | 2008-08-19 | 2010-04-29 | Tour James M | Methods for Preparation of Graphene Nanoribbons From Carbon Nanotubes and Compositions, Thin Films and Devices Derived Therefrom |
| CN101973620A (en) * | 2010-09-21 | 2011-02-16 | 上海大学 | Method for removing heavy metal ions in water by using graphene oxide sheet |
| US20120048804A1 (en) * | 2010-08-25 | 2012-03-01 | Lockheed Martin Corporation | Perforated graphene deionization or desalination |
Family Cites Families (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US7968191B2 (en) * | 2004-03-15 | 2011-06-28 | Cabot Corporation | Modified carbon products and their applications |
| US9169579B2 (en) * | 2005-03-11 | 2015-10-27 | New Jersey Institute Of Technology | Carbon nanotube mediated membrane extraction |
| KR101813170B1 (en) * | 2011-04-11 | 2017-12-28 | 삼성전자주식회사 | Separation membrane comprising graphene |
-
2012
- 2012-03-16 US US13/422,753 patent/US20130240355A1/en not_active Abandoned
-
2013
- 2013-03-06 SG SG10201607771VA patent/SG10201607771VA/en unknown
- 2013-03-06 CA CA2864727A patent/CA2864727A1/en not_active Abandoned
- 2013-03-06 KR KR1020147028957A patent/KR20140138963A/en not_active Withdrawn
- 2013-03-06 SG SG11201404934RA patent/SG11201404934RA/en unknown
- 2013-03-06 AU AU2013232453A patent/AU2013232453A1/en not_active Abandoned
- 2013-03-06 EP EP13709724.2A patent/EP2825507A1/en not_active Withdrawn
- 2013-03-06 CN CN201380014413.9A patent/CN104203835A/en active Pending
- 2013-03-06 IN IN7265DEN2014 patent/IN2014DN07265A/en unknown
- 2013-03-06 WO PCT/US2013/029361 patent/WO2013138137A1/en not_active Ceased
- 2013-03-06 JP JP2015500463A patent/JP2015516286A/en active Pending
- 2013-03-16 SA SA113340389A patent/SA113340389B1/en unknown
-
2014
- 2014-09-11 IL IL234610A patent/IL234610A0/en unknown
Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US20100105834A1 (en) * | 2008-08-19 | 2010-04-29 | Tour James M | Methods for Preparation of Graphene Nanoribbons From Carbon Nanotubes and Compositions, Thin Films and Devices Derived Therefrom |
| US20120048804A1 (en) * | 2010-08-25 | 2012-03-01 | Lockheed Martin Corporation | Perforated graphene deionization or desalination |
| CN101973620A (en) * | 2010-09-21 | 2011-02-16 | 上海大学 | Method for removing heavy metal ions in water by using graphene oxide sheet |
Non-Patent Citations (2)
| Title |
|---|
| ASHISH KUMAR MISHRA等: "Functionalized graphene sheets for arsenic removal and desalination of sea water", 《DESALINATION》 * |
| FRANCESCO FORNASIERO等: "Ion exclusion by sub-2-nm carbon nanotube pores", 《PNAS》 * |
Cited By (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110869109A (en) * | 2017-07-14 | 2020-03-06 | 国立大学法人信州大学 | Nano-window structure of graphene and method for manufacturing high-purity gas |
| US11278849B2 (en) | 2017-07-14 | 2022-03-22 | Shinshu University | Graphene nanowindow structure and method for producing highly pure gas |
| CN108219397A (en) * | 2017-12-27 | 2018-06-29 | 复旦大学 | A kind of method for improving polyethylene terephthalate crystalline rate |
| CN108219397B (en) * | 2017-12-27 | 2020-05-26 | 复旦大学 | A kind of method for improving polyethylene terephthalate crystallization rate |
| CN114901591A (en) * | 2020-03-05 | 2022-08-12 | 寿控股有限公司 | Carbon material and method for producing carbon material |
| CN114901591B (en) * | 2020-03-05 | 2024-05-31 | 株式会社高城 | Carbon material and method for producing carbon material |
| US12090448B2 (en) | 2020-03-05 | 2024-09-17 | Takagi Co., Ltd. | Carbon material and method for producing carbon material |
Also Published As
| Publication number | Publication date |
|---|---|
| US20130240355A1 (en) | 2013-09-19 |
| IN2014DN07265A (en) | 2015-04-24 |
| CA2864727A1 (en) | 2013-09-19 |
| AU2013232453A1 (en) | 2014-09-25 |
| IL234610A0 (en) | 2014-11-30 |
| SG10201607771VA (en) | 2016-11-29 |
| WO2013138137A1 (en) | 2013-09-19 |
| SG11201404934RA (en) | 2014-10-30 |
| EP2825507A1 (en) | 2015-01-21 |
| JP2015516286A (en) | 2015-06-11 |
| KR20140138963A (en) | 2014-12-04 |
| SA113340389B1 (en) | 2015-12-20 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN104203835A (en) | Functionalization of graphene holes for deionization | |
| JP5882327B2 (en) | Deionization or desalination with perforated graphene | |
| US9067811B1 (en) | System, method, and control for graphenoid desalination | |
| US9833748B2 (en) | Perforated graphene deionization or desalination | |
| CN104245098B (en) | Flat Filtration and Selective Separation and Recovery Units | |
| CN104334260A (en) | Selectively perforated graphene membranes for compound harvest, capture and retention | |
| CN104254388B (en) | For filtering and the tunable laminated graphene film configuration of Selective Separation and retracting device | |
| CN101595064B (en) | Desalination method and device comprising supercapacitor electrodes | |
| JP2015515369A5 (en) | ||
| WO2011068611A2 (en) | Nanoengineered field induced charge separation membranes and methods of manufacture thereof | |
| TWI641413B (en) | Separation apparatus and separation method using graphene | |
| Duranceau | Charting the future course for reverse osmosis and nanofiltraton membranes–opportunities and challenges |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C06 | Publication | ||
| PB01 | Publication | ||
| C10 | Entry into substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| C02 | Deemed withdrawal of patent application after publication (patent law 2001) | ||
| WD01 | Invention patent application deemed withdrawn after publication |
Application publication date: 20141210 |